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HomeMy WebLinkAboutWI0300210_Monitoring (Report)_20150923V�/ r 0300210 EOS® Injection and 2 2 20�� Se i- nn Groundwater Monitoring Report Former ATL Site No. 2-66 SEP 2 3 2015 auali� Re910T�a+ Water O�erati;Q�s Se \\\�`tH CARO !/oi ``�O���F E S Slp�•.`��i��/i 41:•:-Y SEAL 25069 ••'•.^;G 1 NEED °• �k,```. �df0i/.* 164 Bostian Bridge Road Statesville, North Carolina H&H Job No. DOT-504 September 4, 2015 14 hart P%• hickman SMARTER ENVIRONMENTAL SOLUTIONS #C-1269 Engineering #-245 Geology 2923 South Tryon Street, Suite 100 3334 Hillsborough Street Charlotte, NC 28203 Raleigh, NC 27607 I www.harthickman.com 704.586.0007 main 919.847.4241 main cl� Via Email September 4, 2015 NC DOT — Roadside Environmental 4809 Beryl Road Raleigh, NC 27606 Attention: Mr. Ethan Caldwell, LG and PE Re: Semi -Annual Monitoring Report NC DOT Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Dear Ethan: Per your request, please find the attached EOS® Monitoring Report for the above -referenced site. information, please do not hesitate to contact me. Sincerely, Hart & Hickman, PC //XY Matt Bramblett, PE Principal Attachment hart '� hickman SMARTER ENVIRONMENTAL SOLUTIONS SEA' 2 2 2015 All REDEIVEDIDENRIDWR SEP 2 3 2015 Water Quality Regionai Ooerations Sect:cr. Injection and Semi -Annual Groundwater If you have any questions or need further cc: Ms. Debra Watts, DWR UIC Program (via certified mail and email) Mr. Andrew Pitner, Mooresville DWR (via certified mail) Mr. Allen Johnson, Property Owner (via certified mail) Ms. Jane Murray, Iredell County Health Department (via certified mail) 2923 South Tryon Street, Suite 100 3334 Hillsborough Street Charlotte, NC 28203 Raleigh, NC 27607 www.harthickman.com 704.586.0007 main 919.847.4241 main EOSO Injection and Semi -Annual Groundwater Monitoring Report Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Table of Contents Section Pate No. 1.0 Introduction..................................................................................................................................1 2.0 Potential Receptor Survey Update.............................................................................................3 2.1 Water Supply Wells....................................................................................................................3 2.2 Surface Water..............................................................................................................................4 3.0 Groundwater/Surface Water Monitoring................................................................................. .5 3.1 Data Collection Procedures........................................................................................................ Is 3.2 Groundwater Levels and Flow Direction................................................................................... 6 3.3 Surface Water Measurements and Analytical Data.................................................................... 6 3.4 Groundwater Analytical Data..................................................................................................... 7 4.0 Evaluation of Natural Attenuation Parameters........................................................................9 4.1 Competing Electron Acceptors...................................................................................................9 4.2 Geochemical Indicator Parameters...........................................................................................12 4.3 Electron Donor..........................................................................................................................14 4.4 Presence of Degradation Daughter Products............................................................................14 5.0 Summary and Conclusions.......................................................................................................16 3ECEIVEDIDENRIDWR SAP 2 3 2015 Water Quality Regiona• Ooeratiols Sector, ' hart hickman S:\AAA-!Master Projec&NC DOT-DOT\DOT-500s Contract\DOT-503 Statesville 66\May 2015 Report\Semi-Am ml GWM Repoa.doc 11-IfF !NV'NVN`Ar Neat Sow n:1NS List of Tables Table 1 Water Supply Well Inventory Table 2 Water Supply Well Analytical Data Summary Table 3 Water Level Data Summary Table 4 Surface Water Analytical Data Summary Table 5 Saprolite Monitoring Well Analytical Data Summary Table 6 Shallow Bedrock Monitoring Well Analytical Data Summary Table 7 Summary of Natural Attenuation Indicator Data Table 8 Surface Water Parameters List of Figures Figure 1 Site Location Map Figure 2 Site Map Figure 3 Water Supply Well Location Map Figure 4 EOS® Injection Point Locations Figure 5 Estimated Shallow Groundwater Potentiometric Map (February 2015) Figure 6 Target VOC Concentrations in Saprolite Groundwater Figure 7 Target VOC Concentrations in Bedrock Groundwater List of Appendices Appendix A Laboratory Analytical Data Appendix B TCE Concentration Trends ii hart' hickman SAAAA-blaster Pzojects`\C DOT-DOT%DOT-500s Coutract\DOT-504 Statesville 603,by 2015 RepoRLSemi-An l GWM Report.doc SMARTER ERMONMENTAL SOLUNONS EOS® Injection and Semi -Annual Groundwater Monitoring Report Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 1.0 Introduction On behalf of the North Carolina Department of Transportation (DOT), Hart & Hickman, PC (H&H) has prepared this report to present post -injection groundwater monitoring data for the former Asphalt Testing Laboratory Site No. 2-66. The site is located at 164 Bostian Bridge Road, which is near Buffalo Shoals Road (State Road 1004) in Statesville, North Carolina (Figure 1). A site map is provided as Figure 2. Soil and groundwater impacts from former asphalt testing operations were previously identified at the site. The asphalt testing utilized trichloroethene (TCE), 1, 1, 1 -trichloroethane (1,1,1-TCA), and/or carbon tetrachloride (CTC). The approved CAP included excavation for source area soil and monitored natural attenuation (MNA) for groundwater impacts. Approximately 162 tons of impacted soils were removed from the source area in September 2001 as reported in H&H's Semi -Annual Monitoring and Soil Remediation Report dated February 19, 2002. Confirmation soil samples indicated that soils were adequately removed. Monitored natural attenuation, consisting of semi-annual or annual groundwater monitoring, was conducted at the site from 2002 until prior to the bioenhancement injection in December 2012. Because TCE concentrations remained more than two orders of magnitude above the groundwater standard, a stream is located near the plume, and there is no public water available in the area of the site, H&H recommended that the bioenhancement event be conducted in shallow groundwater where TCE concentrations were the highest. Bioenhancement improves subsurface conditions for more efficient natural attenuation by reductive dechlorination. On behalf of DOT, H&H prepared an Underground Injection Control (UIC) Permit Application dated August 24, 2012 to conduct a bioenhancement injection at the site. The injectant selected 1 hart hckman SAAAA-Master Proje BBC DOT-DOTtDOT-500s Contract'DOT-504 StatesvWe 661May 2015 Report\Sewi-Amoral GNAt Report.doc -- SMARTER ENVIRONMENTAL SOLUTIONS for the bioenhancement injection event was Emulsified Oil Substrate (EOS®). DENR issued the UIC permit on November 9, 2012. The bioenhancement injection activities were conducted in December 2012. The injection event included 36 temporary direct push technology (DPT) injection points and injecting the EOS® into the upper 20 ft of the saturated zone. The 36 temporary DPT injection wells were installed approximately 20 ft apart perpendicular to groundwater flow and approximately 35 ft apart parallel to groundwater flow within the target treatment area. The DPT temporary injection wells were advanced to depths ranging from approximately 27 ft to 42 ft below ground surface (bgs). The injection area and injection well locations are depicted on Figure 4. The EOS® concentrate was mixed with water prior to injection using an approximate mixing ratio of 1:6 (EOS® to water). For the project, a total of approximately 1,618 gallons of EOS® concentrate were mixed with approximately 10,666 gallons of potable water and injected into the subsurface. The quantity of EOS® was determined using EOS Remediation, LLC's EOS® Design Tool (Version 3.0) software. Approximately 323 to 508 gallons of diluted EOSO mixture were injected into each injection well. This post -injection semi-annual groundwater monitoring report includes a summary of post - injection groundwater monitoring between July 2014 and February 2015. 2 hart hickman &VILAA-Master Projects\NC DOT-DOTtDOT-500s Coatract%DOT-504 Statesville 66\ML ay 2015 Report\Semi-Auuual GNL1 Report.doc SMARTER ENVIRONMENTAL SOLUTIONS 2.0 Potential Receptor Survey Update A summary of area receptors is described below and was updated in November 2014. The next annual receptor survey update will be conducted in the second half of 2015. 2.1 Water Supply Wells The November 2014 receptor survey update was performed by reconnaissance within 1,500 ft of the former asphalt -testing laboratory and by contacting the local utility department to confirm that no municipal wells are in the area. During the November 2014 receptor update, no additional water supply wells were identified within 1,500 ft of the site. A total of 18 water supply wells (active, inactive, or abandoned) are located within a 1,500-ft radius of the former asphalt -testing laboratory. The locations of the water supply wells are indicated on Figure 3, and a summary of water supply well information is provided in Table 1. Of the 18 water supply wells, four wells are located on -site and are designated as WSW -I, WSW-2, WSW-4, and WSW-4A. In accordance with the approved CAP, H&H abandoned water supply wells WSW-1 and WSW-2 in September 2001. Water supply wells WSW-4 (deeper) and WSW-4A (shallow) are located approximately 500 ft southeast and upgradient of the source area. WSW-4 serves the entire subject property and WSW-4A is inactive. Target volatile organic compounds (VOCs) have not been detected in WSW-4 including during the most recent sampling event in February 2015 (Table 2). No off -site water supply wells are located downgradient of the former asphalt -testing laboratory. Each of the 14 off -site water supply wells is located upgradient or cross -gradient of the former asphalt laboratory. The closest off -site water supply well (WSW-5) is situated cross -gradient of the site approximately 650 ft southwest of the former asphalt laboratory. One of the 14 off -site water supply wells (WSW-3) is located cross -gradient of the former asphalt -testing laboratory on the Dorothy Davis property (across an unnamed tributary of Third Creek and approximately 1,200 ft northeast of the former laboratory). WSW-3 was 3 hart hickman S:1AAA-Master Projects`NC DOT-DOTIDOT-500s Contract`DOT-504 Statesville 66Way 2015 Report\Semi-Amwl GWIvi Report.doc SMARTER ENVIRONMENTAL SOLunous sampled in September 1997 and again in October 1998. No target compounds were identified in either sample. Further, a deep saprolite monitoring well (DMW-8), located on the same side of the tributary as WSW-3, is not impacted. The lack of impacts in DMW-8 indicates that the tributary acts as an effective hydraulic barrier. Based on the distance from the former laboratory, the known extent of the contaminant plume, and topographic and hydraulic gradient considerations, the potential for site groundwater impacts to affect the off -site water supply wells is considered to be low. 2.2 Surface Water Two surface water bodies are located within a 0.25-mile radius of the subject site (Figures 1 and 3). An unnamed tributary to Third Creek is located approximately 400 ft north of the former laboratory and borders the northern property boundary. In addition, Third Creek is located approximately 600 ft west of the former laboratory and borders the western property boundary. Both of these surface water bodies appear to be discharge locations for site groundwater. In February 1999, surface water samples were collected from both the unnamed tributary and Third Creek at locations along the northern and western property boundaries of the site. In addition, H&H collected a surface water sample (labeled SS-2) in June 2015 from the unnamed tributary of Third Creek (Table 4 and Figure 2). The surface water sample was analyzed for purgeable halocarbons by EPA Method 6200B. Target compounds were not detected in the surface water sample. In addition, groundwater modeling conducted as part of the CAP indicates that target compounds will not be present in these surface waters above surface water quality standards in the future. Recent surface water sampling activities are discussed further in Section 3. 4 hart ` hickman SAAAA-Mmler Proje ONC DOT-DOT\DOT-500s Contra&-DOT-503 Statesville 66�May 2015 ReporttSeuri-Auuoal GVAI Report.doc SMARTER EWRONMENTAI SOLUTIONS I � 3.0 Groundwater/Surface Water Monitoring As outlined in the UIC permit, H&H conducted a pre -injection groundwater monitoring events on February 2 and 3, 2012 and December 7, 2012 to establish a baseline for comparison with post - injection monitoring data. Additionally, H&H performed quarterly post -injection monitoring events in February 2013, April 2013, June 2013, October 2013, January 2014, May 2014, July 2014, November 2014, and February 2015 to assess the performance of the implemented enhanced bioremediation remedy. The April 2013, October 2013, May 2014, and November 2014 quarterly sampling events were comprehensive events as outlined in the UIC permit application. The groundwater sampling procedures and monitoring results for the most recent monitoring event in February 2015 are discussed below. The locations of the monitoring and temporary injection wells are indicated on Figure 4, and monitoring well construction information is provided in Table 3. 3.1 Data Collection Procedures H&H sampled deeper saprolite monitoring wells DMW-1, DMW-2, DMW-6, DMW-8, DMW-9, DMW-10, and DMW-11 and bedrock monitoring well DMW-7. Additionally, bedrock monitoring well DMW-3, which could not be located during the November 2014 sampling event, was located with a metal detector and sampled. Samples from these wells were submitted for laboratory analysis of VOCs by Environmental Protection Agency (EPA) Method 6200B (reporting the EPA Method 601 list), nitrate, sulfate, sulfide, methane, ethane, ethee, Resource Conservation and Recovery Act (RCRA) metals (arsenic, barium, cadmium, chromium, lead, selenium, silver, and mercury), and total organic carbon (TOC). Field measurements were also collected from these wells and the unnamed tributaryof Third Creek for dissolved oxygen DO Yg ( ), oxidation-reduction potential (ORP), specific conductivity, ferrous iron, pH, and temperature. In addition, one surface water sample was collected from the unnamed tributary of Third Creek located north of the site for laboratory analysis of VOCs by EPA Method 6200B (reporting the EPA Method 601 list) on June 2, 2015. 5 hart hickman &NAAA-:-faster Proje tsWC DOT-DOTIDOT-500s ContraefDOT-504 Statesville 66tMay 2015 Report\Seni-Annual GR'Xf Report.doc SMARM EAMRONMENTAL SOLUTIONS The sampling event was conducted using the following procedures. After monitoring well water levels were gauged, DO concentrations were measured using a downhole probe. Following DO measurements and prior to collection of groundwater samples, the target wells were purged using dedicated disposable bailers until pH, temperature, and specific conductivity levels stabilized. If a well went dry during purging, the purging process was considered to be complete. Groundwater samples were collected with dedicated disposable bailers. Groundwater samples were submitted for laboratory analyses of VOCs using methods listed above. Pace Analytical Laboratories, Inc., a North Carolina -certified laboratory, conducted the laboratory analyses. Dedicated laboratory -supplied sample bottles were used for sample collection. A chain -of -custody record was completed for samples collected and included sample description, date collected, time collected, matrix, sample container information, and analyses required. The chain -of -custody was signed by H&H and placed along with the samples in a chilled cooler for hand delivery to the laboratory by H&H. Copies of the laboratory analytical data sheets and chain -of -custody records are provided in Appendix A. 3.2 Groundwater Levels and Flow Direction Water levels in site monitoring wells were gauged using an electronic water level meter on February 3, 2015 (Table 3). The estimated saprolite potentiometric map constructed from the February 2015 groundwater elevation data is presented as Figure 5. The potentiometric map was constructed using both shallow and deeper saprolite water levels. Consistent with previous data, groundwater flow in the saprolite aquifer is generally to the northwest in the direction of Third Creek and its tributary. The shallow groundwater has a calculated horizontal hydraulic gradient of approximately 0.04 ft/ft. 3.3 Surface Water Measurements and Analytical Data As required in the UIC permit, quarterly surface water measurements were collected from the unnamed tributary of Third Creek at locations upstream (SS-1) and downstream (SS-2) of the injection area to determine if the bioenhancement injection activities are adversely impacting the - 6 hart 0-S. hickman SAAAA-Master ProjectsV\C DOT-DOT\DOT-500s ContracPDOT-504 Statesville GG\May 2015 Report\Senti-Anmwl GNbi Report.doc SMARTER EM+iAONM€Mnl SOLUTIOt75 creek. The locations of SS-1 and SS-2 are depicted on Figure 2. Based on similar data between the two locations during each sampling event, the bioenhancment injection has not adversely impacted the tributary (Table 8). H&H will continue to collect surface water field measurements at locations upstream and downstream of the injection area on a quarterly basis. Should field measurements indicate impacts to the tributary, surface water samples would be collected from the tributary and analyzed for various parameters as outlined in the UIC permit. As outlined in the UIC permit application, a surface water sample was collected from the unnamed tributary of Third Creek at a location (SS-2) downgradient of the injection area on June 2, 2015. The sample was collected by lowering a bailer into the flowing stream. No VOCs were detected in the surface water sample (Table 4). 3.4 Groundwater Analytical Data Deeper Saprolite Analytical results from the February 2015 sampling event indicate groundwater impacts above groundwater standards in deeper saprolite monitoring wells DMW-6 and DMW-11 (Table 5 and Figure 6). TCE and 1,1-dichloroethane were the only two compounds detected above groundwater standards. The most elevated concentrations were detected in DMW-6. TCE was detected in monitoring well DMW-6 at a concentration of 41.8 µg/l, which is above the groundwater standard for TCE of 3 1. 1,1-DCA was detected in monitoring g well DMW-6 at a concentration of 42.3 µg/l, which is above the groundwater standard for of 6 µgll Consistent with previous sampling events, target compounds were not detected in deeper saprolite well DMW-8. Monitoring well DMW-8 is situated on the northern side of the unnamed tributary of Third Creek. The absence of groundwater impacts in DMW-8 indicates that the tributary is acting as an effective hydraulic barrier. hart hickman SAAAA-Master Projects`,NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 Reporf Senti-Auuuat GWNI Report,doc SMARTER EWRtONMENTAt SOLUTIONS Bedrock In February 2015, target compounds were not detected above laboratory reporting limits in bedrock wells DMW-3 and DMW-7 (Table 6 and Figure 7), or in the on -site water supply well WSW4 (Table 2). Additionally, target compounds were not detected above laboratory reporting limits in bedrock well DMW-4 that was last sampled in November 2014. Bedrock well DMW-7 is located adjacent to deep saprolite well DMW-6, which is the monitoring well with the highest target compound concentrations. Although only approximately 25 ft separates the DMW-6 and DMW-7 well screens, the concentrations decrease with depth to non -detectable levels in DMW-7. Concentration Trends TCE is the most widespread target VOC detected above standards. Post -injection February 2015 data indicate that TCE levels have decreased from 68.5 µg/1 to 41.8 µg/1 in DMW-6, 3.3 µg/1 to 3 µg/l .in DMW-9, and 10.8 µg/1 to 7 µg/1 in DMW-11 since the injection in 2012. These trends indicate that the EOS® injection has resulted in enhanced bioremediation within portions of the groundwater plume area. Concentration trends will continue to be evaluated n t d dun future g p g sampling events. Concentrations of key VOCs in saprolite and bedrock groundwater are depicted on Figures 6 and 7. A graph showing the showing the TCE concentration trend in monitoring well DMW-6 is provided in Appendix B. - 8 hart hickman SAAAA-blaster Projects`NC DOT-DOTIDOT-500s ContractlDOT-504 Statesville 661May 2015 ReportUSemi-Ammel GWM Report.doc SMARTER ENVIRONMENTAL SOLUTIONS 4.0 Evaluation of Natural Attenuation Parameters Natural attenuation of groundwater contaminants occurs by physical, chemical, and biological processes. Biodegradation by reductive dechlorination is a primary degradation pathway for the type of constituents present at the site. Additional data on reductive dechlorination including indicator parameter data and daughter product concentrations are discussed below. The target potential DOT compounds at the site are amenable to natural attenuation. 1,1,1-TCA and TCE predominantly biodegrade under anaerobic conditions by a process known as reductive dechlorination. 1,1,1-TCA also degrades abiotically to 1,1-DCE. Historically, there was some evidence of natural degradation of these compounds based on the presence of potential daughter products: 1,1-DCE, l,l-DCA, and cis-1,2-DCE. However, natural site conditions were not highly favorable for reductive dechlorination. The EOSO injection was designed to enhance conditions for biodegradation of the constituents of concern, and general favorable results in concentrations trends are being observed since the injection of EOS® in December 2012. Recent and historical biodegradation data are presented in Table 7. A discussion of the recent indicator parameter data from February 2015 is provided below. 4.1 Competing Electron Acceptors Various electron acceptors can potentially compete with reductive dechlorination, including DO, nitrate, sulfate, iron (III), and carbon dioxide (methanogenesis). Each sequential reaction reduces the ORP of the groundwater into the range within which anaerobic reductive dechlorination can occur most efficiently. These parameters or their byproducts (e.g., Fe(11) and methane) were measured to assess the prevailing redox conditions at the site. A brief discussion of each parameter is provided below. 9 hart ► hickman SAAAA-Master Projects NC DOT-DOTIDOT-500s ContradOOT-504 Statesville 661May 2015 ReportVSewma i-Aml GWbi Report.doc SMARTER ENVIRONMENTAL SOttPflOPiS Dissolved Oxygen DO is used by microbes as an electron acceptor for the biodegradation of organic carbon. Reductive dechlorination occurs under anaerobic or low DO conditions. DO concentrations close to or less than 1 mg/l are favorable. Dissolved oxygen measurements ranged from 0.97 mg/l (DMW-1) to 3.51 mg/1 (DMW-8) in February 2015. Monitoring wells with dissolved oxygen levels close to or less than 1.0 mg/1 included monitoring wells DMW-1, DMW-2, and DMW-6. The measured dissolved oxygen concentrations in most impacted monitoring wells indicate conditions conducive for reductive dechlorination to occur. Nitrate/Nitrite Nitrate may be used as an electron acceptor for anaerobic biodegradation via denitrification. In this process, nitrate is reduced and nitrite is produced. In general, nitrate concentrations in the plume less than background are considered indicative of anaerobic biodegradation. At concentrations greater than 1 mg/l, nitrate may compete with the reductive dechlorination process. Nitrate was detected at concentrations which ranged from <0.020 mg/l (DMW-6, DMW-10 and DMW-11) to 2.70 mg/1 (DMW-2) in February 2015. These data suggest that nitrate reduction may be occurring in the plume, indicating the presence of anaerobic conditions favorable for reductive dechlorination. Most nitrate levels were less than 1 mg/l, and the potential for significant competition with reductive dechlorination is low. Sulfate/Sulfide Sulfate also may be used as an electron acceptor for anaerobic biodegradation. This process is known as sulfate reduction and results in the depletion of sulfate and production of sulfide in the aquifer. Sulfate concentrations within the plume below background concentrations and sulfide concentrations within the plume above background concentrations are indicative of anaerobic 10 S:UAA-T-faster Projects'NC DOT-DOTIDOT-500s Contrace-DOT-504 Statesville 66\May 2015 RepoRlSemi-Amwl GWM Report.doc hart hickman SMARTER ENVIRONMENTAL SOLUTIONS degradation by sulfate reduction. In addition, sulfate at concentrations greater than 20 mg/1 may compete with reductive dechlorination processes. Sulfate was detected at concentrations that ranged from 4.3 mg/l (DMW-1) to 118 mg/l (DMW- 7) in February 2015. Sulfate concentrations in the plume wells were generally greater than the concentration (<20 mg/1) considered most favorable for reductive dechlorination. In general, sulfate concentrations in the plume wells appear to indicate the potential for competition with reductive dechlorination. Sulfide was detected at concentrations which ranged from <0.10 mg/1 (DMW-1, DMW-2, DMW-3, DMW-6, DMW-9, and DMW-7) to 0.25 mg/1 (DMW-2) in February 2015. The low levels of sulfide concentrations in the plume wells appear to indicate that sulfate reduction is not significant anaerobic process at the site. Iron Iron reduction is an anaerobic process in which Fe" is reduced to Fe". The reduced form of iron is soluble. The presence of ferrous iron in groundwater greater than 1.0 mg/l is typically considered an indication of iron -reducing conditions. In February 2015, ferrous iron was generally not detected (<0.2 mg/1), other than 2 mg/l in DMW-10 and 8.5 mg/l in 'MW-11. Therefore, iron reduction appears to be occurring in some portions of the groundwater plume. Methane The presence of methane above background conditions indicates microbial degradation (methanogenesis) is occurring and strongly reducing conditions have been established. The fastest rates of anaerobic dechlorination typically occur under methanogenic conditions. Methane was detected at concentrations which ranged from <6.6 µg/l (DMW-2, DMW-7, and DMW-8) to 4,560 µg/l (DMW-11) in February 2015. These results indicate that strongly reducing conditions are present in portions of the plume. &NAAA-:faster Projects`\C DOT-DOTDOT-500s Contrac0DOT-504 Statesville GG\May 2015 Report\Senti-Amoral OWN1 Report.doc hart hickman SMARTER ENVIRONMENTAL SOLUTIONS 4.2 Geochemical Indicator Parameters Parameters that are indicators of conditions favorable for anaerobic biodegradation of chlorinated solvents include ORP, pH, and temperature. Ethene/ethane (end products) can also serve as indicators of complete reductive dechlorination. At the request of DENR, site wells also were sampled for eight RCRA (metals arsenic, barium, cadmium, chromium, lead, selenium, silver, and mercury). A summary of these data and recent previous natural attenuation indicator and target COC data are provided in Table 7. These parameters (February 2015 data) were evaluated to assess biodegradation processes at the site, and the results are discussed below. Redox Conditions QRP) The ORP of groundwater is a measure of electron activity and is an indicator of "the relative tendency of a solution to accept or transfer electrons. ORP of a groundwater system affects biodegradation rates. Reductive dechlorination is most efficient in the ORP range corresponding to sulfate reduction and methanogenesis (<-100 mV), but reductive dechlorination also occurs in the ORP range associated with nitrate, manganese, and iron reduction (-50 mV to 740 mV). ORP ranged from -32 mV (DMW-11) to 225 mV (DMW-1) in February 2015. ORP data are generally lower in impacted wells and are within the range in which reductive dechlorination may occur. PH and Temperature Groundwater pH values ranging from six to eight standard units are generally preferable for anaerobic biodegradation. The pH of groundwater affects the presence and activity of microbial populations. Acid generated during reductive dechlorination can decrease pH levels after a bioenhancement injection. Groundwater pH ranged from 5.79 to 11.72 in February 2015. The site pH values are within or close to the range, which is considered favorable for reductive dechlorination. 12 hart hickman S:tAAA-Master Proj"&NC DOT-DOT\DOT-500s Coutrace-DOT-504 Statesville 6GWay 2015 Report%ervi :Amual G% 1 Report.doc SMARTER EWRONMENTAL SOLUTIONS Temperature does notgreatly influence reductive dechlorination, but temperatures greater than n 20°C may accelerate biochemical processes. In February 2015, temperatures ranged from 12YC to 18.4°C. The average groundwater temperature for the site is approximately 14.4°C. These temperatures are in the range, which is considered satisfactory for biodegradation. Ethene and Ethane The dissolved gases ethene and ethane are non -toxic end products of reductive dechlorination of chlorinated solvents. Apart from ethane in DMW-6, DMW-10, and DMW-11, dissolved ethene and ethane were not detected in the site wells in the pre -injection or post -injection monitoring events. Ethane was detected in DMW-11 during pre -injection sampling in February 2012 and post -injection sampling in February and April 2013. Additionally, ethane was detected in DMW- 6 during the post -injection sampling in October 2013, January 2014, and February 2015, and in DMW-10 in February 2015. These results indicate that reductive dechlorination may be occurring in the vicinity of DMW-6, DMW-10, and DMW-11. Because ethene and ethane are highly volatile, it is not usual that these compounds were not detected in the remaining plume groundwater samples even if they may have been present in groundwater at low levels. RCRA Metals In February 2015, the RCRA metals barium, cadmium, chromium, and lead were detected in select site wells above pre -injection metals concentrations detected in December 2012. At the request of H&H, the metal concentrations were subsequently confirmed by the analytical laboratory. The RCRA metal concentration increases may be associated with elevated turbidities noted in the monitoring wells. Additionally, because RCRA metal concentration increases were also noted in monitoring wells located greater than 100 ft upgradient of the injection area, the increases do not appear to be related to the 2012 bioenhancement injection. RCRA metals will continue to be evaluated during future sampling events. 13 &NAAA-(Master ProjecteNC DOT-DOT\DOT-500s CgatracPDOT-504 Statesville 66\May 2015 Report\Semi .Aim=l G\VM Report.doc hart 01 hickman SMARTER ENVIRONMENTAL SOWTIONS 4.3 Electron Donor TOC TOC is utilized as an electron donor in the reductive dechlorination process and, therefore, is needed to drive the process. Organic carbon can be either naturally occurring or introduced artificially. The goal of the EOS injection was to provide a carbon source to drive the reductive dechlorination process. The presence of TOC at concentrations greater than 20 mg/L is considered ideal for biodegradation of chlorinated solvents. In February 2015, TOC levels ranged from 3.2 mg/l (DMW-9) to 20.9 mg/1(DMW-11). The TOC levels near the injection area appear to have been enhanced by the injection. H&H will continue to will monitor for the presence of TOC in other portions of the plume during future monitoring events. Metabolic Acids In groundwater, fermentation of EOS produces metabolic acids including lactic, pyruvic, acetic, propionic, and butyric acids. The production of these acids releases hydrogen into groundwater, which is then utilized by indigenous microbes in reductive dechlorination. In January 2014, groundwater samples were analyzed for metabolic acids to evaluate the presence of EOS breakdown products. The metabolic acid results are summarized in Tables 8. Metabolic acids were generally not detected in plume wells in January 2014. In accordance with the UIC monitoring plan, the first year of post -injection sampling has been completed; therefore, metabolic acids are no longer monitored. 4.4 Presence of Degradation Daughter Products Degradation or daughter products have been detected in site groundwater. The presence of the 1,1,1-TCA daughter product 1,1-DCA and TCE daughter product cis-1,2-dicholoroethene (cis- 1,2-DCE) provide direct evidence that biodegradation by reductive dechlorination of the parent VOCs has occurred. In general, daughter product concentrations continue to be present in higher 14 hart hickman SAAAA-Master Projects`NC DOT-DOT\DOT-500s ContracV.DOT-504 Staten Ue 66\May 2015 Report4Semi-AmwI GNVbi Report.doc SMARTER ENVIRONMENTAL SOWNONS concentrations relative to parent products. The continued presence of these daughter products indicates that reductive dechlorination is occurring. In addition to reductive dechlorination, 1,1,1-TCA also undergoes significant degradation by abiotic processes in which it is transformed to 1,1-DCE or acetate in the presence of water. The presence of significant 1,1-DCE concentrations compared to TCA in well DMW-6 indicates that abiotic degradation of TCA is also occurring in the plume area. 15 hart hickman SAAAA-'Master Projects�NC DOT-DOTIDOT-500s ContracttDOT-504 Statesville 66\May 2015 RepoitSemi-Annual GNVM Report.doc SMARTER EWRONMENTAt. SOUMONS 5.0 Summary and Conclusions H&H has implemented an enhanced bioremediation remedy and completed the pre -injection baseline and quarterly post -injection performance monitoring events at the former Asphalt Testing Laboratory Site No. 2-66 in Statesville, NC. The purpose of the remedial action was to address chlorinated solvents in groundwater. The pre -injection baseline monitoring event was completed in February/December 2012 and post -injection performance monitoring events are being conducted. The following summarizes the results of the sampling events and performance of the bioenhancement injection activities: 0 Groundwater impacts, including TCE, l,l,l-TCA, and their daughter products, are present near and downgradient of the former asphalt testing laboratory. Groundwater impacts exceed groundwater standards in two deeper saprolite monitoring wells. No impacts above standards were detected in bedrock monitoring wells. • No ground water impacts were detected in monitoring well DMW-8 located on the opposite side of the unnamed tributary of Third Creek from the former asphalt -testing laboratory. The absence of ground water impacts in DMW-8 indicates that the tributary is acting as an effective hydraulic barrier. 0 Target compounds were not detected in the active, upgradient on -site water supply well or in the unnamed tributary of Third Creek in February 2015 or June 2015, respectively. • A bioenhancement agent (EOS®) was injected into 36 injection wells in December 2012. Post -injection data collected most recently in February 2015 indicate that TCE concentrations are decreasing in plume wells DMW-6, DMW-9, and DMW-11. These trends indicate that the EOS' injection has resulted in enhanced bioremediation within portions of the groundwater plume area. Concentration trends will continue to be evaluated during future sampling events. 16 hart ► hickman S:1AAA-Duster ProjectA C DOT-DOTIDOT-500s Contract'DOT-503 StatenUe 66Way 2015 ReportLSenri-Annual GNDf Report.doc SMARTER ENVIRONMENTAL SOLUTIONS In accordance with the UIC permit, H&H has completed two years of post -injection quarterly performance monitoring. The EOS® injection has been effective at reducing groundwater parent COC concentrations and continued reduction in parent COCs is expected in the future. As a result, H&H is reducing the ground water monitoring schedule from quarterly to semi-annually. The next ground water monitoring event will be conducted in August 2015 with a monitoring report submitted to DOT in Fall 2015. During the sampling event, groundwater samples will be collected from deeper saprolite monitoring wells DMW-1, DMW-2, DMW-6, DMW-8, DMW-9, DMW-10, and DMW-11; and bedrock monitoring wells DMW-3, DMW-4, and DMW-7. Groundwater samples will be submitted to a North Carolina certified laboratory for analysis of VOCs by EPA Method 6200B, reporting only the EPA Method 601 halogenated VOC list and RCRA metals. Due to the extensive amount of natural attenuation data collected during the post - injection quarterly performance monitoring, natural attenuation parameter sampling will be reduced to select measurements including TOC, DO, pH, ORP, and temperature. H&H also will collect a groundwater sample from the active on -site water supply well WSW-4 and the creek located on the northern portion of the site during the August 2015 sampling event. The water supply well will be purged for approximately 15 minutes prior to sample collection. The samples will also be analyzed for EPA Method 601 halogenated VOCs by EPA Method 6200B. 17, SAAAA-Mfaster Projects\NC DOT-DOMOT-500s Contract\DOT-504 Statesville WAlay 2015 Report%enu-Avoail GWbi Report.doc hart hickman SMARTER ENVIRONMENTAL SOLUTIONS Table 1 Water Supply Well Inventory Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Map ID Well Owner & Address Well Status Distance and Direction from Former Asphalt Testing Laboratory WSW-1 Maymead, Inc., 164 Bostian Bridge Drive, Statesville Abandoned On -site, near former asphalt laboratory WSW-2 Maymead, Inc., 164 Bostian Bridge Drive, Statesville Abandoned On -site, near former asphalt laboratory WSW-3 Dorothy Davis, 124 Bostian Bridge Drive, Statesville Active --1,200 ft, cross -gradient WSW-4 Maymead, Inc., 164 Bostian Bridge Drive, Statesville Active On -site, —500 ft, upgradient WSW-4A Maymead, Inc., 164 Bostian Bridge Drive, Statesville Inactive On -site, —500 ft, upgradient WSW-5 Lance & Melissa Lingle, 913 Buffalo Shoals Road, Statesville Active —650 ft, cross -gradient WSW-6 Fred Davis, Buffalo Shoals Road, Statesville Active —800 ft, upgradient WSW-7 Fred Davis Estate, Buffalo Shoals Road, Statesville Active —1,000 ft, upgradient WSW-8 Dorothy Davis, 868 Buffalo Shoals Road, Statesville Active —1,100 ft, upgradient WSW-9 Dorothy Davis, 868 Buffalo Shoals Road, Statesville Active —1,100 ft, upgradient WSW-10 Jerry Hinson, 917 Buffalo Shoals Road, Statesville Active —900 ft, upgradient WSW-11 Jack & Betty Wooten, 897 Buffalo Shoals Road, Statesville Active —1,000 ft, upgradient WSWA2 Margaret Cloer, 881 Buffalo Shoals Road, Statesville Active —1,200 ft, upgradient WSW-13 Jack & Betty Wooten, 871 Buffalo Shoals Road, Statesville Active —1,200 ft, upgradient WSW-14 Jack & Betty Wooten, 865 Buffalo Shoals Road, Statesville Active —1,400 ft upgradient WSW-15 Jerry Hinson, 911 Buffalo Shoals Road, Statesville Active —900 ft, upgradient WSW-16 Wooten Family of NC, 847 Buffalo Shoals Road, Statesville Active —1,200 ft, upgradient WSW-17 Garland Cloer, 889 Buffalo Shoals Road, Statesville Active —1,200 ft, upgradient Notes: Owner and address information based on Iredell County GIS Database and recent H&H windshield survey. WSW-15 and WSW-16 were located during the updated receptor survey in August 2006. WSW-17 was located during the updated receptor survey in August 2010. Water supply well locations are provided on Figure 3. Table 1 (Page 1 of 1) File: S*.~-MasterProjectsWCDOT -DOTDOT-500sContractlDOT-504Statesville 66Way2015RepoMTables\TablesM-WSWinventory Hart &Hickman PC Date: 9*12015 Table 2 Water Supply Well Analytical Data Summary (pg/L) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 WSW-1 (-213') WSW-2 WSW-3 (100') WSW-4 (-165') WSW-4 (-100' Abandoned Site Well Abandoned Site Well Davis Residential Well Site Well (potable) Inactive Site Well 6230D 6230D 601 601(Dup) 601 6230D 601 6230D 601 601 1 601 601 601 601 1 601 601 601 601 601 601 601 601 601 601 601 6200E 6200B 6200B 6200E 62006 6200E 601 COMPOUNDS NC GIN Oct-96 Sep-97 Oct-98 Oct-98 Oct-98 Sep-97 Oct-98 Jan-99 Aug-01 Feb-02 Aug-02 Feb-03 Aug-03 Feb-04 Aug-04 Feb-05 Aug-05 Feb-06 Aug-06 Feb-07 Aug-07 Feb-08 Aug-08 Aug-09 Aug-10 Aug -II Apr-13 Oct-13 May-14 Nov-14 Feb-15 Feb-M Standard 1,1,1-Trichloroethane 200 2 <0.5 <1 <i <1 <0.5 <1 <0.5 <1 <1 <t <1 <1 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 Trichloroethene 3 0.7 <0.5 <1 <1 <1 <0.5 <1 <0.5 <1 <1 < 1 <t <1 <1 <1 <1 <t <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <7.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 1,1-Dichlorcethane 6 0.9 <0.5 <1 <1 <7 <0.5 <1 <0.5 <1 <t <7 <1 <1 <t <t <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 1,1-Dichloroethene 7 0.8 <0.5 <1 <1 <1 <0.5 <1 <0.5 <1 <1 <1 <1 <7 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 Methyl-tert butyl ether 20 1 0.7 NA NA NA <0.5 NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA m/p-xylenes 500 0.5 <0.5 NA NA NA <0.5 NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 1,2,4-Tdmethylbenzene 400 1 <0.5 NA NA NA <0.5 NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA n-Propylbenzene 70 0.9 <0.5 NA NA NA <0.5 NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Naphthalene 6 0.7 <0.5 NA NA NA <0.5 NA 40.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 1,4-Dioxane 3 NA NA NA NA NA NA NA NA NA NA NA NA <5.0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 1,2-Dichloroethane 0.4 0.9 <0.5 <1<1<1<1 <0.5 <t <1 <1 <t <1 <1 <t <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 '1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 Diisopropyl ether 70 0.8 <0.5 NA NA NA dNANA NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Ethylbenzene 600 0.5 <0.5 NA NA NA NA <0.5 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA I NA Notes: Analytical method numbers are shown below sample IDs. NA - Not Analyzed for this parameter. Bold indicates concentration exceeds standard. Dup - Duplicate sample GW - Ground Water Well depth is shown in parenthesis 1,4-Dioxane was analyzed by Method SW846-8260B/SIM Table 2 (Page 1 of 1) File: S:\AAA-Master Projects\NC DOT-DOTIDOT-500s ContractlDOT-504 Statesville 66\May 2015 Report\Tables\Tables\T2-WSW data Hart & Hickman, PC Date: 9/3/2015 Table 3 Water Level Data Summary Former ATL Site No. 2-66 Statesville, North Carolina H& Job No. DOT-504 t,. oc only I 77#r N-TA )niA 1anr-07'7rn1e I KA-A 951d I Miv3n 9014 I Nnvpmhpr5.2014 1 February 3. 2015 Well I.D. Depth (ft) Screen (ft) Screened Aquifer Zone Latitude Longitude ElevationVb TOC (ft) (100 ft DatumOC) ble Water Table Elevation (ft) (100 ft Datum) Static Water Table (ft below TOC Water Table Elevation (ft) 100 ft Datum Static Water Table ft below TOC) Water Table Elevation (ft) 100 ft Datum) Static Water Table ft below TOC Water Table Elevation (ft) 100 ft Datum Static Water Table (ft below TOC Water Table Elevation (ft) 100 ft Datum Static Water Table ft below TOC) Water Table Elevation (ft) 100 ft Datum) Static Water Table ft below TOC Water Table Elevation (ft) 100 ft Datum SMW-1 30 20-30 Shallow Saprolite N35.765483 W80.920233 90.73 64.44 26.70 64.03 27.02 63.71 25.95 64.78 26.87 63.86 27.16 63.57 26.75 63.98 SMW-2 35 25-35 Shallow Saprolite N35.765483 W80.920233 93.92 65.22 29.09 64.83 29.30 64.62 28.30 65.62 29.22 64.70 29.58 64.34 29.22 64.70 SMW-3 40 30-40 Shallow Saprolite N35.765704 W80.919861 98.79 32.05 66.74 32.39 66.40 29.74 69.05 31.29 67.50 32A4 66.35 32.97 65.82 32.68 66.11 SMW-4 35 25 - 35 Shallow Saprolite NA NA 100.52 NM NA NM NA NM NA NM NA NM NA NM NA NM NA SMW-5A 30 20 - 30 Shallow Saprolite NA NA 95.14 NM NA NM NA NM NA NM NA NM NA NM NA NM NA DMW-1 50 45 - 50 Deep Saprolite N35.765396 W80.919907 98.11 32.13 65.98 32.64 65.47 29.91 68.20 31.62 66.49 32.77 65.34 33.23 64.88 32.85 65.26 DMW-2 40 35-40 Deep Saprolite N35.765705 W80.919922 92.72 27.98 64.74 28.39 64.33 28.79 63.93 27.68 65.04 28.55 64.17 28.83 63.89 29.51 63.21 DMW-3 60 55 - 60 Shallow Bedrock NA NA 101.15 28.70 72.45 26.90 74.25 24.16 76.99 24.73 76.42 NM NA NM NA 28.19 72.96 DMW-4 70 65 - 70 Shallow Bedrock N35.765276 W80.919932 98.08 32.13 65.95 32.60 65.48 29.85 68.23 31.66 66.42 32.64 .65.44 33.08 65.00 32.89 65.19 DMW-5 38.5 28.6 - 38.5 Deep Saprolite NA NA 78.57 NM NA NM NA NM NA NM NA NM NA NM NA NM NA DMW-6 36.25 26.25 - 36.25 Deep Saprolite N35.765961 W80.920820 79.60 18.48 61.12 18.75 60.85 18.42 61.18 18.54 61.06 18.88 60.72 18.84 60.76 18.68 60.92 DMW-7 65 60 - 65 Shallow Bedrock N35-765950 W80.920806 81.85 17.66 61.34 17.92 61.08 17.57 61.43 NM NA NM NA NM NA 22.04 59.81 DMW-8 24 14 - 24 Deep Saprolite N35.766168 W80.921506 68.34 7.76 60.58 8.00 60.34 7.70 60.64 7.77 60.57 8.20 .60.14 8.15 60.19 7.86 60.48 DMW-9 40 3040 Deep Saprolite N35.765726 W80.920251 88.72 25.53 63.19 25.84 62.88 25.38 63-34 25.42 63.30 NM INA NM NA 27-33 61.39 DMW-10 38 28-38 Deep Saprolite N35.765725 W80.920812 86.24 25.32 60.92 25.68 60.56 25.36 60.88 25.61 60.63 25.86 60.38 25.81 60.43 25.61 60.63 DMW-11 40 30-40 Deep Saprolite N35.766114 W80.920408 85.13 23.30 61.83 23A9 61.64 23.21 61.92 23.99 61.84 23.47 81.66 26.65 58.48 23-44 61.69 noies: TOC = Top of PVC well casing. All wells referenced to an assumed datum of 100 feet. NA - Not Available/Not Applicable NM - Not Measured SMW-5A was abandoned March 21, 2002 DMW-3, DMW4 and DMW-7 are Type III double -cased wells. DMW-1, DMW-3 and DMW4 were repaired on 7/24/06 and re -surveyed for TOC elevations on 8/17/06 DMW-5 discovered damaged in August 2008 and could not be sampled. SMW4 could not be located since December 2012. DMW-7 was repaired on 9/16/14 and re -surveyed for TOC elevation on 11/6/14 Table 3 (Page 1 of 1) Fle: S?AAA-Mier PrcjmMWC DOT-DOTDOT-500s Ca WMOT-504Sta-ft WlMy2015RpW:Tab1%Ueb1es\T3-Weta Tale Hart & Hickman, PC Data 93MIS Table 4 Surface Water Analytical Data Summary Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Compound SS-1 Upgradient Tributary SS-2 Downgradient Tributary SS-3 Upgradient Third Creek SSA Mid -Point ThirdCreek SS-5 Downgradient Third Creek Feb-99 Feb-99 Au -01 Au -02 Au -03 Au -04 Au -05 Au -06 Au -07 Au -08 Feb-09 Au -09 Au -10 Au -11 A r-13 Oct-13 Ma -14 Jun-15 Feb-99 Feb-99 Feb-99 14-Dioxane NA NA NA NA NA <5.0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 111-Tdchloroethane <0.5 <0.5 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <0.5 <0.5 <0.5 Trichloroethene <0.5 <0.5 <1 <1 <t <1 <1 <11.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <0.5 <0.5 1 <0.5 1 1-Dichloroethane <0.5 <0.5 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <0.5 <0.5 <0.5 cis-1 2-Dichloroethene <0.5 <0.5 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 41.0 <1.0 <1.0 <1.0 <1.0- <1.0 <1.0 <0.5 <0.5 <0.5 1 1-Dichloroethene <0.5 <0.5 <1 <1 <1 <1 <1 <1.0 <1.0 <1.0 <1.0 I <1.0 <1.0 <1.0 <t.o <1.0 I <1.0 <1.0 -0.5 <0.5 <0.5 Chloroform <0.5 <0.5 1 <1 <1 <1 <1 <1 I <1.0 <1.0 <1.0 1 11.0 1 <1.0 <1.0 <1.0 <1.0 <1.0 I <1.0 <1.0 <0.5 <0.5 <0.5 N Ies: Results are in pgll "<" indicates compound was not detected above the analytical detection limit NA - Not Analyzed for this parameter. Table 4 (Page 1 of 1) File: S:1AAA-Master Projects\NC DOT-DOTDOT500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T4-Surface Water Summary Hart &Hickman PC Date: 9/3/2015 Table 5 (Page 1 of 6) Saprolite Monitoring Well Analytical Data Summary (lag/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trichloroethane Trichloroethene 1,1-Dichloroethane 1,2-Dichloroethane 1,1-Dichloroethene cis-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride Chlorobenzene WELL SCREEN INTERVAL Well ID Analysts Sample Date 601 Dec-96 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Oct-98 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -01 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-03 <1 <1 <1 <1 <l <1 NA <5 <1 601 Au -D3 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-04 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -04 <1 <1 <1 <1 <1 <1 <5.0 <5 <1 NS Feb-06 NS NS NS NS NS NS NS NS NS 601 Au -06 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 SMW-1 601 Feb-07 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA i <2.0 <1.0 SS (15'-25') 601 Au -07 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 601 Feb-08 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -08 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Feb-09 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -09 -1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -10 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <5.0 <1.0 6200E Au -11 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B A r-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Oct-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Ma -14 <1.0 <1.0 <1.0 <1.0 -1.0 <1.0 NA <2.0 <1.0 6200E Nov-14 <1.0 <1.0 <1.0 <1.0 <1.0 -1.0 NA <2.0 <1.0 601 Dec-96 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Oct-98 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -01 <1 <1 4.3 <1 1.9 <1 NA <5 <1 601 Feb-02 <1 <1 3.7 <1 <1 <t NA <5 <1 601 Au -02 <1 <1 4.8 <1 1.8 <1 NA <5 <1 601 Feb-03 <1 <1 8.1 <1 2.7 <1 NA <5 <1 601 Au 03 <1 <1 11 <1 <1 <1 NA <5 <1 601 Feb-04 <1 <1 8.9 <1 1A <1 NA <5 <1 601 Aug-0 <1 <1 8.2 <1 0.961 <1 <5.0 <5 <1 601 Feb-05 <1.0 <1.0 5.9 <1.0 <1.0 <1 NA <1.0 <1.0 601 Au -05 <1 <1 8.8 <1 <1 <1 NA <2 <1 601 Feb-06 <1 <1 6.7 <1 <t <1 NA <2 <1 SMW-2 601 Au -06 <1.0 <1.0 5.6 <1.0 <1.0 <1.0 NA <2.0 <1.0 SS (20'-3D') 601 Feb-07 <1.0 <1.0 4.7 <1.0 <1.0 <1.0 NA <2.0 1 <1.0 601 Au -07- <1.0 <1.0 3.5 <1.0 <1.0 <1.0 NA <2.0 <1.0 601 Feb-08 <1.0 <1.0 3.8 <1.0 -1.0 <1.0 NA <1.0 <1.0 601 Au -08 <1.0 <1.0 3.1 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Feb-09 <1.0 <1.0 3.5 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -09 <1.0 <1.0 1.9 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -10 <1.0 <1.0 5.8 <1.0 <1.0 <1.0 NA <5.0 <1.0 601 Au -10 <1.0 <1.0 5.8 <1.0 <1.0 <1.0 NA <5.0 <1.0 6200E Au -11 <1.0 -1.0 2.1 <1A <1.0 -1.0 NA <2.0 <1.0 6200E Apr-1 3 <1.0 <1.0 2.2 <1.0 <1.0 <1.0 NA <2.0 <1.0 62008 Oct-13 <1.0 <1.0 2.0 <1.0 <1.0 <1.0 NA -2.0 <1.0 8200B Ma -14 <1.0 <1.0 3.1 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Nov-14 <1.0 <1.0 2.2 <1.0 <1.0 <1.0 NA <2.0 <1.0 NC GW Standard 200 3 6 0.4 350 70 3 5 50 rvares: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs. 1,4-Dioxane was analyzed by Select ton Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater; NA = Not Analyzed for this parameter; NS = Well not sampled J= The analyte was positively identified but the value is estimated below the reporting limit SMW-5A was abandoned March 21, 2002 SMW4 is damaged and could not be sampled, August 2004; SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78J µgA, August 2004 Vinyl chloride (1.7 ug/1) and 1,1,2-trichloroethane (1.8 ug/1) were detected in DMW-6 in February 2005 Chloroform (3 ugA), and ,1,1,2-trichloroethane (3.5 ug/1) were detected in DMW-6 in February 2006 1,1,2,2-Trichloroethane (2.2 ug/1) was detected in DMW-6 in February 2008 Chloroform (3.5 ugA), and ,1,1,2-tichloroethane (2.5 ug/I) were detected in DMW-6 in August 2009 1,1,2-trichloroethane (1.2 ugA) was detected in DMW-6 in August 2011 Table 5 (Page 1 of 6) File: S:\AW-Master Projects\NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T5-New sap data Date: 9/3/2015 Hatt & Hickman, PC Table 5 (Page 2 of 6) Saprolite Monitoring Well Analytical Data Summary (Ng/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trichloroethane Trichloroethene 1,1-Dichloroethane 1,2-Dichloroethane 1,1-Dichloroethene cis-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride Chlorobenzene WELL SCREEN INTERVAL Well ID Analysis Sample Date 601 Dec96 4 1 1 <1 2 6 NA <5 <1 601 Oct-98 3 <1 10 <1 <1 7 NA <5 <1 601 Au -01 4.4 <1 6.2 <1 <1 <1 NA <5 <1 801 Feb-02 2.3 1.5 8.3 <1 <1 <1 NA <5 <1 801 Au -02 1.8 2.1 11 <1 1.5 2.8 NA <5 <1 801 Feb-03 4.0 1.6 11 <1 <1 1.3 NA <5 <1 801 Au -03 1.1 <1 12 <1 <1 <1 NA <5 <1 601 Feb-04 <1 <1 7.1 <1 <1 2.9 NA <5 <1 601 Au -04 <1 <1 4.7 <1 <1 1.7 <5.0 <5 <1 601 Feb-05 <1.0 <1.0 3.1 <1.0 <1.0 1.9 NA <1.0 <1.0 601 Au -05 <1 <1 5.7 <1 <1 2.8 NA <2 <1 601 Feb-06 <1 <1 7.7 <1 <1 3.0 NA <2 <1 SMW3 601 Au -06 <1.0 <1.0 6.9 <1.0 <1.0 2.8 NA <2.0 <1,0 SS (30'-40') 601 Feb-07 41.0 <1.0 7.7 <1.0 -1.0 2.7 NA <2.0 <1.0 601 Au -07 <1.0 <1.0 6.7 <1.0 <1.0 3A NA <2.0 <1.0 601 Feb-08 <1.0 <1.0 8.7 <1.0 <1.0 2.3 NA <1.0 <1.0 601 Au -08 <1.0 1.5 7.9 <1.0 <1.0 1.9 NA <1.0 <1.0 Fet>09 <1.0 <1.0 8.8 <1.0 -1.0 3.7 NA <1.0 <1.0 Au -09 <1.0 <1.0 4.5 <1.0 <1.0 2.8 NA <1.0 <1.0 L2O Au -10 <1.0 <1.0 4.7 <1.0 <1.0 2.1 NA <5.0 <1.0 Au -11 <1.0 <1.0 3.7 <1.0 <1.0 1A NA <2.0 <1.0 Apr-1 3 <1.0 <1.0 4.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Oct-13 <1.0 0.0 4.3 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Ma -14 <1.0 <1.0 2.1 <1.0 <1.0 <1.0 NA <2.0 <1.0 62008 Nov-14 <1.0 <1.0 2.3 <1.0 <1.0 <1.0 NA <2.0 <1.0 SMW 4 601 Deo-96 <1 <1 <1 <t <1 <1 NA <5 <1 SS (25'35') 601 Oct-98 <1 <1 <1 <1 <1 <1 NA <5 <1 SMW-5A 601 Dec-96 1 <1 <1 <1 6 <1 NA <5 <1 SS (20'30') NC GW Standard 200 3 1 6 1 0.4 350 70 1 3 5 50 11 Notes: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs. 1,4-Dioxane was analyzed by Select Ion Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater; NA = Not Analyzed for this parameter; NS = Well not sampled J= The analyte was positively identified but the value is estimated below the reporting limit SMW-5A was abandoned March 21, 2002 SMW4 is damaged and could not be sampled, August 2004; SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78.1 µg/I, August 2004 Vinyl chloride (1.7 ugn) and 1,1,2-trichloroethane (1.8 ug/1) were detected in DMW-6 in February 2005 Chloroform (3 ug/1), and ,1,1,2-trichloroethane (3.5 ug/1) were detected in DMW-6 in February 2006 1,1,2,2-Trichloroethane (2.2 ug/1) was detected in DMW-6 in February 2008 Chloroform (3.5 ugA), and ,1,1,2-trichloroethane (2.5 ug/1) were detected in DMW-6 in August 2009 1,1,2-trichloroethane (1.2 ug/1) was detected in DMW-6 in August 2011 Table 5 (Page 2 of 6) File: S:\AW-Master Projects\NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T5-New sap data Date: 9/3/2015 Hart & Hickman, PC Table 5 (Page 3 of 6) Saprolite Monitoring Well Analytical Data Summary (Ng/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-604 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trichloroethane Trichloroethene 1,1-Dichloroethane 1,2-Dichloroethane 1,1-Dichloroethene cis-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride I Chlorobenzene WELL SCREEN INTERVAL Well ID Analysis Sample Datc 601 Dec-96 53 47 26 <1 37 53 NA <5 1 8260B Jan-97 59 54 28 <5 51 59 NA <5 <5 601 Oct-98 30 41 28 <1 40 59 NA <5 <1 801 Au -01 110 110 61 <1 51 56 NA <5 <1 601 Feb-02 88 84 31 <1 64 58 NA <5 <1 601 Au -02 42 51 23 <1 36 30 NA <5 <1 601 Feb-03 17 28 16 <1 17 21 NA <5 <1 601 Au -03 27 49 30 <1 27 39 NA <5 <1 601 Feb-04 4.2 8.9 9.1 <1 8.8 10 NA <5 <1 601 Au -04 2.8 5.8 5.3 <1 4.5 7.4 <5.0 <5 <1 601 Feb-05 2.7 7.4 6.1 <1.0 6.3 9.7 NA <2.0 <1.0 NS Au -OS I NS NS NS NS NS NS NS NS NS NS Feb-06 NS NS NS NS NS NS NS NS NS 601 Au -06 1.5 5.8 4.9 <1.0 2.4 4.9 NA <2.0 <1.0 601 Feb-07 1.8 5.3 4.9 <1.0 3.0 7.2 NA <2.0 <1.0 601 Au -07 11.0 1.4 2.0 <1.0 1.2 2.7 NA <2.0 <1.0 DS (45'-50') DMW-1 601 Feb-08 <1.0 2.1 1.7 <1.0 1.2 2.7 NA -1.0 <1.0 801 Aug- 8 <1.0 2.4 1.2 <1.0 2.0 1.8 NA <1.0 <1.0 601 Feb-09 1.2 3.8 4.7 <1.0 3.2 4.4 NA <1.0 <1.0 601 Au -09 <1.0 2.9 1.9 <1.0 1.8 2.5 NA <1.0 <1.0 601 Au -10 4.0 3.5 4.7 <1.0 3.8 4.8 NA <5.0 <1.0 62008 Aug-1 1 <1.0 2.4 3.7 <1.0 1.7 3.5 NA <2.0 <1.0 62009 Feb-12 <1.0 1.3 1.8 <1.0 <1.0 1.6 NA <2.0 <1.0 8200E Feb-13 <1.0 1.0 1.3 <1.0 -1.0 1.1 NA <2.0 <1.0 6200E A r-13 <1.0 1.0 1.8 <1.0 <1.0 1.1 NA <2.0 <1.0 62008 JunA3 <1.0 1.0 2.8 <1.0 <1.0 2.0 NA <2.0 <1.0 62006 Oct-13 <1.0 1.9 3.7 <1.0 1.3 2.8 NA <2.0 <1.0 6200B Jan-14 <1.0 3.0 4.5 <1.0 <1.0 3.3 NA <2.0 <1.0 62008 Ma -14 <1.0 1.6 2.9 <1.0 <1.0 2.0 NA <2.0 <1.0 8200B Jul-14 <1.0 2.1 4.2 <1.0 1.3 3.5 NA <2.0 <1.0 6200E Nov-14 <1.0 1.0 2.4 <1.0 <1.0 1.9 NA <2.0 <1.0 6200B Feb-15 <1.0 1.2 2.5 <1.0 <1.0 2.0 NA <2.0 <1.0 NC GW Standard 1 200 1 3 6 0.4 350 70 3 5 1 50 Notes: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs. 1,4-Dioxane was analyzed by Select Ion Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater; NA = Not Analyzed for this parameter; NS = Well not sampled J= The ahalyte was positively identified but the value is estimated below the reporting limit SMW-5Awas abandoned March 21, 2002 SMW-4 is damaged and could not be sampled, August 2004; SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78J µgA, August 2004 Vinyl chloride (1.7 ugA) and 1,1,2-trichloroethane (1.8 ugA) were detected in DMW-6 in February 2005 Chloroform (3 ugA), and ,1,1,2-trichloroethane (3.5 ugA) were detected in DMW-6 in February 2006 1,1,2,2-Trichloroethane (2.2 ug/1) was detected in DMW-6 in February 2008 Chloroform (3.5 ug/1), and ,1,1,2-trichloroethane (2.5 ug/1) were detected in DMW-6 in August 2009 1,1,24richloroethane (1.2 ugA) was detected in DMW-6 in August 2011 Table 5 (Page 3 of 6) File: S:kW-Master Projects\NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T5-New sap data Date: 9/3/2015 Hart & Hickman, PC Table 5 (Page 4 of 6) Saprolite Monitoring Well Analytical Data Summary (Ng/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trtchloroethane Triehloroethene 1,1-Dichloroethane 1,2-Dichloroethane 1,1-Dichloroethene . cls-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride Chlorobenzene WELL SCREEN INTERVAL Well ID Analysis Sample Dat 601 Mar-97 210 120 72 <2.5 130 <2.5 NA <12.5 <2.5 601 Oct-98 29 18 48 <1 39 <1 NA <5 <1 601 Au -01 9.9 11 43 <1 17 1.7 NA <5 <1 601 Feb-02 23 18 49 <1 32 <1 NA <5 <1 601 Au -02 21 22 55 <1 32 5.1 NA <5 <1 601 Feb-03 12 17 23 <1 13 2.8 NA <5 <1 601 Au -03 21 37 94 <1 23 <1 NA <5 <1 601 Feb-04 13 28 73 <1 18 6.6 NA <5 <1 601 Au -04 27 48 86 <1 38 15 <5.0 <5 <1 601 Feb-05 18 38 40 <1.0 32 12 NA <2.0 <1.0 601 Au -OS 20 38 67 <1 19 12 NA <2 <1 601 Feb-06 15 42 59 <1 19 9.1 NA <2 <1 601 Au -06 13 29 58 <1.0 14 12 NA <2.0 <1.0 601 Feb-07 8.2 19 40 <1.0 11 8.3 NA <2.0 <1.0 601 Au -07 4.3 10 37.8 <1.0 6.2 4.2 NA <2.0 <1.0 DMW-2 601 Feb-08 2.1 6.6 22 <1.0 3.0 2.8 NA <1.0 <1.0 DS (35'-40') 601 Au -08 1.4 5.0 17 <1.0 3.2 2.1 NA <1.0 <1.0 601 Feb-09 2.1 5.8 16 <1.0 4.5 3.0 NA <1.0 <1.0 601 Au -09 1.6 5.8 9.2 <1.0 3.2 1.9 NA <1.0 <1.0 601 Au -10 4.8 4.3 8.9 <1.0 3.5 1.9 NA <5.0 <1.0 6200B I Aug-1 1 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Feb-12 <1.0 <1.0 2.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Feb-13 <1.0 <1.0 1.6 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Apr-13 <1.0 <1.0 2.1 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Jun-13 <1.0 <1.0 1.8 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Oct-13 <1.0 <1.0 1.8 <1.0 -1.0 <1.0 NA <2.0 <1.0 6200E Jan-14 I <1.0 <1.0 1.3 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Ma -14 <1.0 <1.0 1.3 <1.0 <1.0 <1.0 NA -2.0 <1.0 6200B Jul-14 <1.0 -1.0 1.1 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Nov-14 <1.0 <1.0 1.2 <1.0 -1.0 <1.0 NA <2.0 -1.0 62006 Feb-15 <1.0 <1.0 1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6230D Jan-99 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 NA <5 <0.5 601 Au-01 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-03 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -03 <1 <1 <1 <1 <1 <1 NA <5 <1 DS (28.5'- DMW-5 601 Feb-04 <1 <1 <1 <1 <1 <1 NA <5 <1 38.5') 601 Au -04 <1 <1 <1 <1 <1 <1 <5.0 <5 <1 601 Feb-05 <1.0 <1.0 <1.0 <1.0 <1.0 <1 NA <2.0 <1.0 601 Au -05 <1 <1 <1 <1 <1 <1 NA <2 <1 601 Feb-06 <1 <1 <1 <1 <1 <1 NA <2 <1 601 Au -06 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 NECW Standard 200 3 6 1 0.4 350 70 3 5 50 Notes: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs.1,4-Dioxane was analyzed by Select Ion Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater, NA = Not Analyzed for this parameter, NS = Well not sampled J= The analyte was positively identified but the value is estimated below the reporting limit SMW-5A was abandoned March 21, 2002 SMW-4 is damaged and could not be sampled, August 2004; SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78J µgA, August 2004 Vinyl chloride (1.7 ugA) and 1,1,2-trichloroethane (1.8 ugA) were detected in DMW-6 in February 2005 Chloroform (3 ugA), and ,1,1,2-trichloroethane (3.5 ug/l) were detected in DMW-6 in February 2006 1,1,2,2-Trichloroethane (2.2 ugA) was detected in DMW-6 in February 2008 Chloroform (3.5 ugA), and ,1,1,2-trichloroethane (2.5 ugA) were detected in DMW-6 in August 2009 1,1,2-trichloroethane (1.2 ug/I) was detected in DMW-6 in August 2011 Table 5 (Page 4 of 6) File: S:\AAA-Master Projects\NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T5-New sap data Date: 9/3/2015 Hart & Hickman, PC Table 5 (Page 5 of 6) Saprolite Monitoring Well Analytical Data Summary (Ng/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trichloroethane Trichloroethene 14-Dichloroethane 1,2-Dichloroethane 1,1-Dichloroethene cis-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride Chlorobenzene WELL SCREEN INTERVAL Well iD I Analysis SampleDate 6230D Jan-99 74 67 42 <0.5 160 1.5 NA <5 <0.5 601 Au -01 95 57 60 <1 93 4.5 NA <5 <1 601 Feb-02 140 170 89 <1 500 <10 NA <5 <10 801 Au -02 140 190 120 <1 590 18 NA <5 <10 801 Feb-03 100 160 77 <1 430 <10 NA <5 <10 Au -03 97 170 80 4.3 420 14 NA 8.5 <1 Feb-04 63 140 74 <1 350 10 NA <5 <1 K Au -04 61 150 74<10 380 8.1J 180 <50 <10 Feb-05 49 150 69 7.8 250 10 NA 5.6 <1.0 Au -05 65 170 83 <5 290 12 NA <10 1 <5 601 Feb-06 44 220 98 1.8 390 9.2 180 5.8 <1 601 Au -06 19 190 83 <5 270 9.0 NA -10 <5.0 601 Feb-07 39 170 81 <5 330 12.0 180 <10 <5.0 601 Au -07 40.3 157 100 <10.0 290 <10.0 NA <20.0 <10.0 601 Feb•08 33 130 77 <1.0 200 6.9 170 <1.0 <1.0 DS (26.25'- DMW-6 601 Au -08 24 100 77 3.6 180 6.1 NA <1.0 <1.0 36.25') 601 Feb-09 18 96 67 <1.0 220 6.7 NA <1.0 <1.0 601 Au -09 23 120 83 4.9 220 6.6 NA <1.0 <1.0 601 Aug-10 16 100 79 <1.0 200 8.6 NA <5.0 <1.0 6200E I Au -11 10.6 100 75.9 1.3 147 3.9 NA <2.0 <1.0 6200E I Feb-12 5.9 68.5 53.1 <1.0 90.5 3.0 NA <2.0 <1.0 62008 Feb-13 5.2 71.8 61.6 <1.0 92.1 3.7 NA <2.0 <1.0 6200B A r-13 5.5 71.4 65.0 1.1 99.2 3.8 NA <2.0 <1.0 6200E Jun-13 5.1 67.1 67.8 <1.0 92.7 3.0 NA <2.0 <1.0 6200B Oct-13 5.0 69.9 71.1 1.1 97.7 4.3 NA <2.0 <1.0 6200B Jan-14 3.6 62.5 50.9 1.2 73.2 3.5 NA <2.0 <1.0 6200B Ma -14 3.1 64.9 57.2 <1.0 67.7 1.9 NA <2.0 <1.0 6200E Jul-14 1.9 43.2 40.6 <1.0 52.0 2.5 NA <2.0 <1.0 6200B Nov-14 2.0 46.7 47.5 <1.0 59.7 3.3 NA <2.0 <1.0 6200B Feb-15 1.5 41.8 42.3 <1.0 55.0 2.7 NA <2.0 <1.0 601 Au -01 <7 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -02 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-03 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -03 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Feb-04 <1 <1 <1 <1 <1 <1 NA <5 <1 601 Au -04 <1 <1 <1 <1 <1 <1 <5.0 <5 <1 601 Feb-05 <1 <1 <1 <1 <1 <1 NA <1.0 <1 801 Au -05 <1 <1 <1 <1 <1 <1 NA <2 <1 601 Feb-06 <1 <1 <1 <1 <1 <1 NA <2 <1 601 Au -06 <1.0 <1.0 <1.0 <1.0 <1.0 -1.0 NA <2.0 <2.0 601 Feb-07 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <2.0 601 Au -07 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 601 Feb-08 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 DMW-8 801 Au -08 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 DS (14'-24') 601 Feb-09 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -09 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 601 Au -10 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <5.0 <1.0 8200B Au -11 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Feb-12 <1.0 <1.0 <1.0 <11.0 <1.0 <1.0 NA <2.0 <1.0 6200E Feb-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 62008 A r-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 62008 Jun-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA -2.0 <1.0 8200E Oct-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Jan-14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Ma -14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Jul-14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA -2.0 <1.0 62008 I Nov-14 <1.0 I <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 620013 1 Feb-15 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 NC GW Standard 200 3 6 0.4 350 70 3 5 50 Notes: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs. 1,4-Dioxane was analyzed by Select Ion Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater, NA = Not Analyzed for this parameter, NS = Well not sampled J= The analyte was positively identified but the value is estimated below the reporting limit SMW-5A was abandoned March 21, 2002 SMW-4 is damaged and could not be sampled, August 2004: SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78J jig/I, August 2004 Vinyl chloride (1.7 ug/1) and 1,1,2-trichloroethane (1.8 ugh) were detected in DMW-6 in February 2005 Chloroform (3 ug/I), and ,1,1,2-trichloroethane (3.5 ug/1) were detected in DMW-6 in February 2006 1,1,2;2-Trichloroethane (2.2 ugA) was detected in DMW4b in February200B Chloroform (3.5 ug/l), and ,1,1,2-trichloroethane (2.5 ug/l) were detected in DMW-6 in August 2009 1,1,24richloroethane (1.2 ug/1) was detected in DMW-6 in August 2010 Vinyl chloride (1.5 ug/I) was detected in DMW-6 in November 2014 Table 5 (Page 5 of 6) File: S:\AAA-Master Projects\NC DOT-DOT\DOT-500s Contract\DOT-504 Statesville 66\May 2015 ReporhTables\Tables\T5-New sap data Date: 9/3/2015 Hart & Hickman, PC Table 5 (Page 6 of 6) Saprolite Monitoring Well Analytical Data Summary (jig/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 DOT Target Compounds Non -Target COMPOUND 1,1,1-Trichloroethane Trichloroethene 1,1-Dichloroethane 1,2-Dfchloroethane 1,1-Dichloroethene cis-1,2-Dichloroethene 1,4-Dioxane Methylene Chloride Chlorobenzene WELL SCREEN Well ID at sis Sample DateINTERVAL 6200E Feb-12 <1.0 3.3 4.5 <1.0 2.1 <1.0 NA <2.0 <1.0 6200B Feb-13 11.0 5.8 8.5 <1.0 3.6 <1.0 NA <2.0 <1.0 6200E Apr-13 <1.0 6.4 7.7 <1.0 4A 1.1 NA <2.0 <1.0 6200E Jun-13 <1.0 5.5 6.7 <1.0 3.6 1.2 NA <2.0 1 <1.0 DMW-9 6200B Oct-13 <1.0 4.9 4.9 <1.0 3A 1.2 NA <2.0 <1.0 DS (30'-40') 6200E Jan-14 <1.0 2A 2.6 -1.0 1.9 <1.0 NA <2.0 <1.0 6200B Ma -14 <1.0 2.9 2.3 <1.0 1.9 <1.0 NA <2.0 <1.0 6200B Nov-14 <1.0 2.6 2.3 <1.0 1.6 <1.0 NA <2.0 <1.0 62008 Feb-15 1 <.0 3.0 2.2 <1.0 1.3 <1.0 NA <2.0 <1.0 6200E Feb-12 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Feb-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E A r-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Jun-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Oct-13 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 DS DMW-10 6200E Jan-14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 (30'40') 6200B Ma -14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200E Jul-14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Nov-14 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Feb-15 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <2.0 <1.0 6200B Feb-12 <1.0 10.8 10.9 <1.0 15.0 <1.0 NA <2.0 <1.0 6200B Feb-13 <1.0 8.0 7.0 <1.0 10.5 <1.0 NA <2.0 <1.0 6200B Apr-1 3 <1.0 9.0 7.6 <1.0 11.9 <1.0 NA <2.0 <1.0 6200B Jun-13 <1.0 5.7 4.9 <1.0 7.4 1.4 NA <2.0 <1.0 6200B Oct-13 <1.0 6.3 6.6 <1.0 9.0 <1.0 NA <2.0 <1.0 DS DMW-11 6200B Jan-14 <1.0 8.1 6.8 <1.0 9.5 <1.0 NA <2.0 <1.0 (30'-40') 6200B May-14 <1.0 6.3 5.4 <1.0 7.5 <1.0 NA <2.0 <1.0 6200E Jul-14 I <1.0 7.9 8.6 <1.0 11.0 <1.0 NA <2.0 <1.0 62008 Nov-14 -1.0 9.8 10 <1.0 13.2 <1.0 NA <2.0 <1.0 6200B Feb-15 <1.0 7.0 %7 <1.0 9.5 <1.0 NA <2.0 <1.0 NC GW Standard 200 3 6 0.4 350 70 3 5 50 Notes: Bold indicates concentration exceeds standard Analytical method numbers are shown beside sample IDs. 1,4-Dioxane was analyzed by Select Ion Monitoring SS - Shallow Saprolite; DS - Deep Saprolite; GW - Groundwater; NA = Not Analyzed for this parameter; NS = Well not sampled J= The analyte was positively identified but the value is estimated below the reporting limit SMW-5A was abandoned March 21, 2002 SMW-4 is damaged and could not be sampled, August 2004; SMW-4 repaired July 2006 DMW-2 reported Chloroform at an estimated value = 0.78J µg/1, August 2004 Vinyl chloride (1.7 ug/1) and 1,1,2-trichloroethane (1.8 ugA) were detected in DMW-6 in February 2005 Chloroform (3 ug/I), and ,1,1,2-trichloroethane (3.5 ug/I) were detected in DMW-6 in February 2006 1,1,2,2-Trichloroethane (2.2 ug/1) was detected in DMW-6 in February 2008 Chloroform (3.5 ugA), and ,1,1,2-trichloroethane (2.5 ug/1) were detected in DMW-6 in August 2009 1,1,2-trichloroethane (1.2 ug/1) was detected in DMW-6 in August 2011 Table 5 (Page 6 of 6) File: S:~-Master Projects\NC DOT-DOT0OT-500s Contract\DOT-504 Statesville 66\May 2015 Report\Tables\Tables\T5-New sap data Date: 9/3/2015 Hart & Hickman, PC Table 6 Shallow Bedrock Monitoring Well Analytical Data Summary (mg/1) Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 COMPOUND 1,1,1- Trichloroethane Trichloroethene 1,1- Dlchloroethane 1,1- Dichlomethene cis-1,2- Dichla1,2- a 1,4-Dioxane Chlorobenzene WELL SCREEN INTERVAL Well ID Analysis Sample Dale 601 Mar-97 <1 <1 <7 <1 <1 NA <1 601 Oct-98 <1 <1 <1 <1 <1 NA <1 601 Feb-03 <7 <t <1 <1 <1 NA <1 601 Au 3 <1 <i <1 <1 41 NA <1 601 Feb-04 <1 <1 41 <1 <1 NA <1 60118260 Au <1 <1 <1 <1 <1 1 -5.0 <1 601 Feb-05 <1 <1 <1 <1 <1 NA <1 601 Au 5 <1 <1 <1 <1 <1 NA <1 601 Feb-06 <1 41 <1 <1 <1 NA <1 601 Au 6 <1.0 -1.0 <1.0 -1.0 <1.0 NA <1.0 DMW-3 601 Feb-07 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 (55'-601 601 Au <1.0 <1.0 <7.0 <1.0 <7.0 NA <1.0 601 Feb-08 -1.0 <1.0 <1.0 <7.0 <1.0 NA -1.0 601 Au -08 <1.0 <1.0 <1.0 -1.0 1<1.0 NA <1.0 601 Feb-09 <1.0 <1.0 -1.0 <1.0 <1.0 NA <1.0 601 Au 10 <1.0 -1.0 <1.0 <1.0 <1.0 NA <1.o 6200B Aug-1 1 <1.O <1.0 -1.0 <1.0 <1.0 NA -1.0 62008 r-13 <1.0 <7.0 <1.0 <1.0 <1.0 NA <1.0 6200B Oct-13 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 6200E Ma -14 <1.0 <7.0 <1.0 <1.0 <1.0 NA <1-0 6200B Feb-15 <7.o <1.0 <1.0 <1.0 <1.0 NA <1.0 601 Mar-97 <1 <1 <1 <1 <1 NA <t 601 Oct-98 <1 <1 <t <1 <1 NA <1 601 1 Au 1 <1 <7 <1 <1 <1 NA <1 601 Feb-02 <1 <1 41 <1 <1 NA <1 601 Au -02 <1 <1 <1 <1 <1 NA <i 601 Feb-03 <1 <1 <1 <1 <i NA <1 601 3 <1 <1 <1 <1 <1 NA <1 601 Feb-04 <1 <1 <1 <1 <1 NA <1 601/8260 Au <1 <1 <1 <1 <1 <5.0 <1 601 Feb-05 <1 <1 1 1 <1 <1 NA <1 601 Au 05 <1 <1 <1 <1 <1 NA <1 601 1 Feb-06 <1 <1 <1 <1 <1 NA `1 (65'-70') DMW-0 601 Au -1.0 <100 <1.0 <1.0 <1.0 NA <1.0 601 Feb-07 <1.0 <1.0 <1.0 <100 <1.0 NA <1.0 601 Au 07 <1.0 -1.0 <1.0 <1.0 <1.0 NA -1.0 601 Feb-08 -1.0 <1.0 <1.0 <1.0 I <1.0 NA <1.0 601 Au -08 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 601 Au -09 <t.o <7.0 <1.O <1.0 <1.0 NA <1.0 601 Au -10 <1.0 <1.0 <1.0 <7.0 <1.0 NA <1.0 62003 Au 11 <1.0 <1.0 <1.0 <7.0 <1.0 NA <1.0 62006 r-13 <1.0 <1.0 <7.0 <1.0 <1.0 NA <1.0 6200E Oct-13 <1.0 <1.0 <7.0 <1.0 <1.0 NA <1.0 6200B Ma -14 <1.0 <1.0 <1.0 <1.0 <1.0 NA <11.0 6200E Nov-14 <1.0 <7.0 <1.0 <1.0 <1.0 NA <7.0 601 Au 1 <1 <1 <1 <1 I <1 NA <1 601 Feb-02 <1 <1 <1 1.9 <1 NA <1 601 Au 2 2.4 6.3 1.6 14 <1 NA <7 601 Feb-03 2.1 2.4 <t 2.8 <1 NA <1 601 Au 3 3.8 7.0 1.5 12 <1 NA <1 601 Feb-04 <1 1.5 <1 2.6 <1 NA <1 601/8260 Au -04 O.B1J 2.2 0.70J 3.6 <i 45.0 <7 601 Feb-05 <1 2.1 <7.0 3.9 41 NA <1 601 Au o5 <1 1.6 <1 1.9 <1 NA <1 601 Feb-06 <1 3.7 1.5 3 <1 NA <7 601 Au -06 <1.0 4.6 1.3 3.3 <1.0 NA <1.0 601 Feb-07 <1.0 2.2 1.8 2.5 <1.0 NA <1.0 601 1 Au -07 <1.0 2.7 1.2 3.5 <1.0 NA <11.0 601 Feb-08 -1.0 2.2 <1.0 1.6 <1.0 NA <1.0 DMW-7 601 Au 8 <1.0 3.1 <1.0 2.6 <11.0 NA <1.0 (60'-651 601 Feb-09 -1.0 2.3 IA 2.6 <1.0 NA <1.0 601 Au <1.0 2.1 <1.0 1.3 1 <1.0 NA <1.0 601 Au -10 <1.0 3.2 1.1 2.8 <1.0 NA <7.0 6200B Au 11 <1.0 -1.0 <1.0 <1.0 <1.0 NA e1.0 6200E Feb-12 <7.0 <1.0 <1.0 <1.0 <1.o NA <1.0 6200E Feb-13' <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 62008 I A r-13 <1.0 <1.0 <1.0 <1.0 <1.0 NA -1.0 6200E Jun-13 <1.0 <1.0 -1.0 <1.0 <7.0 NA <1.0 6200E Oct-13 <1.0 <1.0 <7.0 <1.0 <1.0 I NA <1.0 8200E Jan-14 <1.O <1.0 <1.0 <1.0 <1.0 I NA I <1.0 6200B Ma -14 <1.0 <7.0 <1.0 <1.0 <1.0 NA <1.0 8200B Jul-14 <7.0 <1.0 <1.0 -1.0 -1.0 NA -1.0 6200E Nov-15 <7.0 <1.0 e1.0 <1.0 <1.0 NA <7.0 6200B Feb15 <1.0 <1.0 <1.0 <1.o <1.0 NA <7.0 NC GW STANDARD 200 1 3 6 350 70 13 50 Analytical method numbers are shown beside sample IDs. Bold indicates concentration exceeds standard GW -Ground Water J= The analyte was positively identified but the value is estimated below the reporting limit NA = Not Analyzed for this parameter - 1,4-Dioxane was analyzed by Method SW 846-8260B(SIM = Methylene chloride detected at a concentration of 2.7 (pg0) in February 2013 Table 6 (Page 1 of 1) rr: swwmmr+genwc oormrmr�osraa..rmraw snes�esxyans wwmrmmrmmre«..eaan Harr & Hickman, PC Table 7 (Page 1 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring Weil ED SMW-1 SMW-2 Sampling Date Au -10 Au -11 A r-13 Oct-13 Ma 44 Nov-14 Aug-10 Au -11 A r-13 Oct-13 Ma 44 Nov-14 Field Measurements Dissolved Oxygen (mg/1) 1.83 3.13 3.50 1.35 1.61 1.23 0.34 0.98 3.20 1.17 1.04 1.88 Ferrous Iron (mg/1) NA NA <0.2 <0.2 <0.2 <0.2 NA NA <0.2 <0.2 1.0 2.0 Redox (mV) 277 278 144.2 320 368.1 313 384 521 280 406 370 398 Conductivity (µS/cm) 130.0 160.0 123.0 157.8 298.0 386.4 288.0 220.0 263.0 270.1 344.9 401.7 pH (standard units) 5.27 5.21 5.13 5.39 5.76 5.86 5.31 5.03 5.22 5.29 5.55 5.86 Temperature (°C) 18.0 18.1 19.3 17.5 18.0 18.4 18.6 19.0 19.6 17.3 18.0 17.7 Labortaory Analytical Parameters NA NA NA NA NA 2.9 NA NA NA NA NA <0.020 Nitrate (mg/1) Sulfate (mg/1) NA NA NA NA NA 20.8 NA NA NA NA NA 54.8 Sulfide (mg/l) NA NA NA NA NA <0.10 NA NA NA NA NA <0.10 TOC (mg/1) NA NA NA NA NA 30.9 NA NA NA NA NA 31.2 Methane (µg/1) NA NA NA NA NA <6.6 NA NA NA NA NA 136 Ethane (µg/l) NA NA NA NA NA <6.2 NA NA NA NA NA <6.2 Ethene (µg/1) NA NA NA NA NA <6.2 NA NA NA NA NA <6.2 Metals 601017470 /ue/D Arsenic NA NA NA NA NA <10.0 NA NA NA NA NA <10.0 Barium NA NA NA NA NA 122 NA NA NA NA NA 34.7 Cadmium NA NA NA NA NA <1.0 NA NA NA NA NA <1.0 Chromium NA NA NA NA NA <5.0 NA NA NA NA NA <5.0 Lead NA NA NA NA NA <5.0 NA NA NA NA NA <5.0 Selenium NA NA NA NA NA <10.0 NA NA NA NA NA <10.0 Silver NA NA NA NA NA <5.0 NA NA NA NA NA <5.0 Mercury NA NA NA NA NA <0.20 NA NA NA NA NA <0.20 Metabolic.4cids ftzlb Acetic Acid NA NA NA NA NA NA NA NA NA NA NA NA Butyric Acid NA NA NA NA NA NA NA NA NA NA NA NA Lactic Acid NA NA NA NA NA NA NA NA NA NA NA NA Propionic Acid NA NA NA NA NA NA NA NA NA NA NA NA Pyruvie Acid NA NA NA I NA I NA I NA I NA I NA NA I NA I NA NA Notes: TOC = Total Organic Carbon; DO = Dissolved Oxygen; NA = Not Analyzed t = Sulfide and metals samples collected on July 17, 2013. File: S.WN Mmtm Pt jmtsWC DOT-0OTXDOTSWs CwnMDOTS04 Ste+esve 66M W2D15 Repro eblm Td*e U7-Nat Atlen. riev Table 7 (Page 1 of 6) Dates 9=15 Half &Hickman, PC Table 7 (Page 2 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring WellID SMW-3 DMW-1 Sampling Date Aug-10 Aug-11 Apr-13 Oct-13 May44 Nov-14 Feb-12 Dec-12 Feb-13 Apr-13 Jun-13t Oct-13 Jan-14 May44 Jul-14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (mg/1) 0.31 0.97 2.22 1.70 1.22 1.68 0.68 NA 2.40 2.48 0.86 1.20 1.11 1.37 1.61 2.11 0.97 Ferrous Iron (mg/1) NA NA <0.2 <0.2 <0.2 <0.2 <0.2 NA <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 Redox(mV) 121 84 107 106 124 176.1 310 NA 296 116 414 320 206 300 319 290 225 Conductivity (µS/cm) 128.0 110.0 123.0 127.1 196.7 298.1 96.4 NA 106.3 73.0 71.4 157.8 70.0 125.5 302.7 361.1 79.4 pH (standard units) 5.34 5.70 5.51 5.58 5.98 5.62 5.64 NA 5.63 5.50 5.56 5.39 5.57 5.25 4.99 5.57 6.03 Temperature (°C) 18.6 19.0 18.2 16.4 16.4 16.3 18.3 NA 18.3 18.2 19.8 17.5 15.7 16.0 15.7 15.2 15.4 Labortaory Analytical Parameters 0.28 NA NA NA NA 0.079 <0.20 NA 0.076 0.079 0.07 0.11 0.23 0.32 0.24 0.041 0.059 Nitrate (mg/1) Sulfate (mg/1) 48 NA NA NA NA 6.4 <5.0 NA 5.2 4.2 4.6 4.2 4.5 3.9 3.6 4.2 4.3 Sulfide (mg/1) NA NA NA NA NA <0.10 NA <0.10 <0.10 NA <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 TOC (mg/1) 2.5 NA NA NA NA 28.8 4.9 NA 26.7 4.9 5.7 4.5 5.5 4.4 6.1 17.4 4.2 Methane (µg/1) NA NA NA NA NA 18.7 15.7 NA 12.8 7.3 8.2 9.3 15.4 14.2 10.2 10.4 13.8 Ethane (µg/1) NA NA NA NA NA <6.2 <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Ethene (µg/1) NA NA NA NA NA <6.2 <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Metals 601017470 6w11) Arsenic NA NA NA NA NA <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 Barium NA NA NA NA NA 107 NA 56.7 58.1 NA 57.5 56.8 60.2 59.8 61.8 54.3 502 Cadmium NA NA NA NA NA <1.0 NA <1.0 <1.0 NA <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 1.2 Chromium NA NA NA NA NA <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 86.4 Lead NA NA NA NA NA <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 27.9 Selenium NA NA NA NA NA <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <I0.0 <10.0 <10.0 <10.0 Silver NA NA NA NA NA <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 Mercury NA NA NA NA NA <0.20 NA <0.20 <0.20 NA <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 Metabolic Acids (me/b Acetic Acid NA NA NA NA NA NA <5.0 NA <1.8 1.91 <0.67 <0.67 <0.67 NA NA NA NA Butyric Acid NA NA NA NA NA NA <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA Lactic Acid NA NA NA NA NA NA <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA Propionic Acid NA NA NA NA NA NA <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA Pyruvic Acid NA NA I NA I NA I NA I NA 1 <10 1 NA i <2.0 1 <2.0 <0.53 i <0.53 <0.53 1 NA I NA I NA I NA Notes: TOC = Total Organic Carbon; DO = Dissolved Oxygen; NA =Not Analyzed t = Sulfide and metals samples collected on hay 17, 2013. Table 7 (Page 2 of 6) Fft S:WAFAbWPrgwftWCDOT -DOTXD0T5aasCmtadCOT567Stdt UoWNW 2015RepaaTableskTables1T7444Aftm.re (2) Hart &Hickman, PC Data. 9=15 Table 7 (Page 3 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring WellED DMW-2 DMW-6 Sampling Date Feb-12 Dec-12 Feb-13 A r-13 Jun-13n Oct-13 Jan-14 Ma -14 Jul-14 Nov-14 Feb-15 Feb-12 Dec-12 Feb-13 A r-13 Jun-13n Oct-13 Jan-14 May-14 Jul-14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (nng/1) 0.41 NA 2.83 3.08 0.83 1.17 1.16 1.66 0.82 0.67 1.41 1.24 NA 3.23 3.32 0.76 1.17 1.06 0.41 1.44 0.76 1.11 Ferrous Iron (ing/1) <0.2 NA <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 NA <0.2 <0.2 <0.2 <0.2 <02 <0.2 <0.2 <0.2 <0.2 Redox(utV) 207 NA 324 242 372 286 197 210 195 191 141 174 NA 91 131 410 136 49 87 106 69 68 Conductivity (ItS/can) 281.6 NA 243.6 263.0 253.9 282.3 234.0 445.6 490.9 578.1 259.8 418.9 NA 363.3 385.0 364.7 410.9 330.0 409.7 425.8 493.7 288.4 pH (standard units) 5.18 NA 5.06 4.84 5.02 5.06 4.94 5.30 5.31 5.00 6.20 6.11 NA 6.26 5.33 6.11 6.15 6.16 6.61 6.97 7.01 6.28 Temperature (°C) 18.6 NA 18.3 18.6 19.6 16.2 15.7 17.1 17.0 16.6 13.0 16.4 NA 16.3 16.7 16.3 15.6 16.0 16.4 17.0 16.4 12.3 Labortaory Analvdcal Parameters 4.50 NA 3.20 5.40 2.90 3.50 3.70 2.40 2.30 2.5 2.7 <0.20 NA 0.59 0.74 0.33 0.86 0.54 <0.020 <0.020 <0.020 <0.020 Nitrate (mg/1) Sulfate (mg/1) 66.8 NA 79.1 60.6 79.5 72.7 79.1 83.3 81.8 69.3 77.2 81.3 NA 62.7 86.9 70.3 54.3 58.2 59.5 45.9 39.8 45.3 Sulfide (mgd) NA <0.10 <0.10 NA <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 NA <0.10 <0.10 NA <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 TOC (mgn) 6.0 NA 5.4 11.4 42.6 5.8 7.0 5.3 5.8 23.6 3.6 10.3 NA 11.8 11.8 11.0 46.0 17.1 11.1 14.2 45.0 8.7 Methane (Itgn) 76.4 NA 105 124 110 62.8 61.9 30.3 <6.6 42.2 58.7 22.2 NA 192 18.9 <6.6 93.8 49.4 17.4 <6.6 766 674 Ethane (Itg/1) <I0.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <10.0 NA <6.2 <6.2 <6.2 7.0 7.0 <6.2 <6.2 7.0 <6.2 Ethene (µgd) <10.0 NA <6.2 <6.2 <6.2 <6.2 <62 <6.2 <6.2 <6.2 <6.2 <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 61.6 Motnis 601017470 (ye/7) Arsenic NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 Barium NA 32.3 27.6 NA 28.4 28.3 28.2 27.2 28.2 26.3 91.0 NA 117 216 NA 114 ill 195 109 108 126 172 Cadnniumn NA <1.0 <1.0 NA <1.0 <1.0 1.0 <I.0 <I.0 <1.0 <1.0 NA <1.0 <I.0 NA <1.0 <1.0 <I.0 <1.0 <1.0 <I.0 <1.0 Chronnitmn NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 212 NA <5.0 37.9 NA <5.0 <5.0 35.7 <5.0 <5.0 <5.0 20.3 Lead NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 5.8 NA <5.0 10.3 NA <5.0 <5.0 10.6 <5.0 <5.0 <5.0 8.9 Selenium NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 Silver NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 Mercury NA <0.20 <0.20 NA <020 0.22 <0.20 <0.20 <0.20 <0.20 <0.20 NA <0.20 <0.20 NA <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 <020 Metabolic Acids (ma Acetic Acid <5.0 NA <1.8 <1.8 <0.67 <0.67 <0.67 NA NA NA NA <5.0 NA <1.8 LK <0.67 <0.67 <0.67 NA NA NA NA Butyric Acid <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA Lactic Acid <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA Propionic Acid <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA jPyruvic Acid I <10 I NA 1 <2.0 1 <2.0 <0.53 1 <0.53 1 <0.53 1 NA I NA NA I NA I <10 I NA <2.0 <2.0 1 <0.53 1 <0.53 1 <0.53 1 NA I NA I NA I NA Notes: TOC = Total Organic Carbon; DO = Dissolved Oeygeu: NA = Not Analyzed t = Sulfide and metals samples collected on Ady 17, 2013. Table 7 (Page 3 of 6) o a:WIAM.nta PropcbWC WT-0OTDOTi00�CanVacl�DOT-sal SlabrnYe 66\May]DIS �pw(�TebbalTffiIn\T)N0.Reen.new (3) o- srnma Hart & Hickman, PC Table 7 (Page 4 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring Well JD DMW-8 DMW-9 Sampling Date Feb-12 Dec-12 Feb-13 A r-13 Jun-131 Oct-13 Jan-14 Ma -14 Jul-14 Nov-14 Feb-15 Feb-12 Dec-12 Feb-13 A r-13 Jun-131 Oct-13 Jan-14 Ma -14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (mg/1) 4.44 NA 4.86 4.98 4.76 3.55 3.10 2.86 2.04 3.01 3.51 0.95 NA 1.01 1.09 1.11 2.45 2.32 2.07 1.71 2.36 Ferrous Hon (mg/1) <0.2 NA <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 0.5 NA <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <02 Redox(mV) 258 NA 94 101 103 116 237 220 197 297 199 ill NA 293 139 314 184 116 112 135 132 Conductivity (pS/cm) 159.8 NA 147.3 150.0 146.0 168.7 142.0 162.8 170.9 198.2 155.3 290.1 NA 245.4 268.0 249.8 283.0 240.0 270.6 313.0 260.2 pH (standard units) 6.51 NA 6.78 6.16 6.10 6.54 6.51 6.62 6.44 6.80 6.61 5.70 NA 5.62 5.40 5.88 5.47 5.53 5.69 5.88 5.79 Temperature (°C) 14.6 NA 16.1 15.0 17.6 16.2 12.6 14.5 15.0 13.9 13.5 182 NA 18.6 18.6 18.4 18.4 17.9 17.8 17.0 14.4 Labortaory Analytical Parameters 0.76 NA 0.77 0.56 0.73 0.72 0.88 0.80 0.79 0.87 0.81 2.1 NA 1.7 1.6 1.5 1.5 1.4 1.5 1.4 1.4 Nitrate (mg/1) Sulfate (mg/1) <5.0 NA 2.6 2.2 2.4 2.3 3.0 2.1 <2.0 2.2 27 61.5 NA 66.7 65.6 85.1 65.8 76.3 71.3 69.3 71.9 Sulfide (ing/1) NA <0.10 <0.10 NA <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 0.20 NA <0.10 <0.10 NA <0.10 <0.50 <0.50 <0.50 <0.10 <0.20 TOC (nig/1) 22.2 NA 2.2 22.1 3.0 2.5 2.1 3.4 24.4 10.8 20.6 7.1 NA 5.7 7.2 5.5 5.5 8.1 5.6 30.6 3.2 Methane (µg/l) <10.0 NA <6.6 <6.6 <6.6 8.3 <6.6 <6.6 <6.6 <6.6 <6.6 147 NA 151 153 24.6 40.6 175 116 707 1,010 Ethane (jig/1) <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <I0.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Ethene (jig/1) <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Meals 601017470 (ae/!) Arsenic NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <I0.0 <10.0 <10.0 Barium NA 60.4 33.8 NA 36.1 35.9 33.6 28.9 30.7 32.3 846 NA 100 91.0 NA 84.3 86.2 85.0 82.0 76.0 896 Cadmium NA <1.0 <1.0 NA <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <I.0 NA <1.0 <1.0 NA <1.0 <1.0 <I.0 <1.0 <1.0 1.1 Chromium NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 81.2 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 209 Lead NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 14.6 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 32.0 Selenium NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <10.0 NA <I0.0 <10.0 <I0.0 <10.0 <10.0 10.0 Silver NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 Mercury NA <0.20 <0.20 NA <0.20 <0.20 <020 <0.20 <0.20 <0.20 <0.20 NA <0.20 <0.20 NA <0.20 <0.20 <0.20 <0.20 <020 0.47 Metabolic Acids (mn/1) Acetic Acid <5.0 NA <1.8 <1.8 <0.67 <0.67 <0.67 NA NA NA NA <5.0 NA <1.8 <1.8 <0.67 <0.67 NA NA NA NA Butyric Acid <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA <5.0 NA <0.87 <0.87 <0.10 <0.10 NA NA NA NA Lactic Acid <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA <25 NA <2.3 <2.3 <2.0 <2,0 NA NA NA NA Propionic Acid <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA <5.0 NA <1.0 <1.0 <0,25 <0.25 NA NA NA NA ,Pynivic Acid <10 I NA 1 <2.0 1 <2.0 1 <0.53 1 <0.53 1 <0.53 1 NA I NA I NA I NA I <10 I NA 1 <2.0 1 <2.0 1 <0.53 1 <0.53 NA I NA NA I NA Notes: TOC = Total Organic Carbon: DO = Dissolved Oxygen; NA = Not Analyzed '= Sulfide and metals samples collected on July 17, 2013. J = estimated concemmtion greater than the method detetion limit. but below the reporting limit. Table 7 (Page 4 of 6) s:-vmwc ooToonoor3aa. c�o-arnmr-sa sw® n, seia=ymts aewmTm�nubm+�. nm,. �.Iq Har! Se Hickman, PC wm smots Table 7 (Page 5 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring WelliD DMW-10 DMW-11 Sampling Date Feb-12 Dec-12 Feb-13 A r-13 Jun-13r Oct-13 Jan-14 Ma -14 Jul-14 Nov-14 Feb-15 Feb-12 Dec-12 Feb-13 A r-13 Jun-13r Oct-13 Jan-14 Ma -14 Jul-14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (mg/l) 2.25 NA 0.88 0.92 0.52 0.82 0.80 1.11 2.01 1.93 2.04 1.03 NA 1.13 1.20 0.83 2.24 2.19 1.99 2.16 2.32 1.70 Ferrous Iron (mg/1) <0.2 NA 5.0 5.0 4.5 5.0 5.0 6.0 5.4 2.5 2.0 0.5 NA 7.5 8.0 8.0 8.5 9.0 10.0 9.0 8.5 8.5 Redox (mV) 22 NA -58 -27 4 -37 -34 -17 -17 -42 -17 18 NA 54 76 116 12 66.4 71.4 93 105 -32 Conductivity (1tS/cm) 463.2 NA 440.0 440.0 428.4 490.6 400.0 381.2 480.1 398.9 423.6 666.8 NA 500.3 556.0 490.4 576.1 492.0 448.9 502.3 427.9 428.3 pH (standard units) 6.51 NA 6.47 6.24 6.34 6.35 6.39 6.61 6.71 6.46 6.50 6.67 NA 6.32 5.70 6.23 6.30 6.15 6.20 6.29 6.13 6.69 Temperature (DC) 18.3 NA 18.9 18.6 18.4 17.6 17.3 17.9 17.0 16.3 13.3 17.3 NA 18.3 17.1 17.3 17.6 16.6 16.8 16.4 16.2 14.6 Labortaory Analvtical Parameters <0.20 NA <0.020 <0.020 <0.020 0.12 <0.020 <0.020 <0.020 <0.020 <0.020 <0.20 NA <0.020 <0.020 <0.020 <0.020 <0.020 <0.020 <0.020 <0.020 <0.020 Nitrate (rng/1) Sulfate (mg/1) 19.0 NA 27.4 22.4 24.9 35.3 20.8 20.2 17.6 18.3 19 114 NA 99.7 106 103 75 108 47.9 80.3 39.2 79.6 Sulfide (mg/1) NA <0.10 0.15 NA <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 0.25 NA <0.10 <0.10 NA <0.10 <0.50 <0.10 <0.10 <0.10 <0.10 0.14 TOC (mg/I) 21.4 NA 24.9 26.0 22.8 18.3 21.6 23.6 27.9 46.1 18.5 23.9 NA 24.2 26.9 25.0 18.4 23.4 23.8 21.9 45.0 20.9 Methane(lig/1) 945 NA 1,040 839 389 701 <6.6 555 1,160 1,200 654 1,640 NA 347 260 65.3 663 3,790 2,140 4,070 4,840 4,560 Ethane (jig/1) <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 14.5 NA 6.5 7.7 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Ethene (µgll) <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 33.6 <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Metals 601017470 (ae/1) Arsenic NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 Barium NA 140 707 NA 1" 136 141 252 143 122 282 NA 88.3 89.7 NA 70.0 69.8 66.5 58.9 69.5 56.1 789.0 Cadmium NA <I.0 8.2 NA <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 NA <1.0 <1.0 NA <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 Chromium NA <5.0 224 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 4.5.7 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 85.0 Lead NA <5.0 92.7 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 22.1 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 110 Selenium NA <10.0 10.8 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 NA <10.0 <I0.0 NA <10.0 <10.0 <10.0 <I0.0 <10.0 <10.0 <10.0 Silver NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 Mercury NA <0.20 <0.20 NA <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 NA <0.20 <0.20 NA <0.20 <0,20 <0.20 <0.20 <0.20 <0.20 <0.20 Meraboltc Acids /m e/D Acetic Acid <5.0 NA <1.8 1.91 <0.67 <0.67 0.67J NA NA NA NA <5.0 NA <1.8 <1.8 <0.67 <0.67 <0.67 NA NA NA NA Butyric Acid <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA Lactic Acid <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA Propionic Acid <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA jPyruvic Acid <10 I NA 1 <2.0 1 <2.0 1 <0.53 1 <0.53 1 <0.53 1 NA I NA I NA I NA I <10 I NA 1 <2.0 1 <2.0 1 <0.53 1 <0.53 1 <0.53 1 NA I NA I NA I NA Notes: TOC = Total Organic Carbon; DO = Dissolved Oxygen; NA = Not Analyzed = Sulfide and metals samples collected on July 17. 2013. J = estimated concentration greater than the method detetion limit. but below the reporting lnnit. Table 7 (Page 5 of 6) D.e S+AA9aaD15 DIs PmptlaWGDDT-0011WTii00, CDnbxADai�501 akttaa➢e 6TMry]015 RepvM1TeDleeRabbalTiWx ADm. mst5) Hart &Hickrnan, PC Dat Table 7 (Page 6 of 6) Summary of Natural Attenuation Indicator Data Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Monitoring We11ID DMW-3 DMW-4 DMW-7 Sampling Date Att -10 Att -11 Oct-13 Ma -14 Feb-15 Au -10 Au -11 I Oct-13 Ma -14 Nov-14 Feb-12 Dec-12 Feb-13 A r-13 Jim-131 Oct-13 Jan-14 Ma -14 Ju1-14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (mg/1) 0.51 0.99 3.58 3.14 3.62 0.24 0.56 1.01 0.99 2.88 1.16 NA 4.37 4.89 3.27 2.76 2.60 2.86 2.70 2.16 2.84 Ferrous Iron (mg/1) NA NA <0.2 <0.2 <0.2 NA NA <0.2 <0.2 1.2 <0.2 NA <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 Redox (ml') NA NA -104.3 -71.9 32.0 NA NA 405.6 400 -46.9 286 NA 101 160 402 148 51 80 106 75 113 Conductivity (pS/cm) 649.0 394.0 300.1 428.9 1,455.0 216.0 203.0 270.1 250.0 288.1 228.6 NA 115.3 113.0 114.3 98.6 111.0 142.9 202.7 199.4 168.6 pH (standard units) 10.69 7.45 10.38 9.62 11.72 6.75 6.71 5.29 5.89 6.67 6.72 NA 6.96 6.28 6.62 6.16 6.96 7.58 7.46 7.58 6.23 Temperature (°C) 18.3 18.6 16.2 16.5 15.4 18.8 18.6 17.3 18.0 16.1 15.6 NA 15.9 17.4 18.0 15.4 15.7 18.4 18.7 18.0 18.4 LabortamT Analytical Parameters NA NA NA NA 0.29 NA NA NA NA NA <0.20 NA 0.50 0.46 0.48 0.032 0.58 0.18 0.61 2.9 0.63 Nitrate (mg/1) Sulfate (ing/1) NA NA NA NA 76.7 NA NA NA NA NA <5.0 NA 4.7 7.4 4.8 10.9 3.8 4.4 5.2 24.9 118 Sulfide (mg/1) NA NA NA NA <0.10 NA NA NA NA NA NA <0.10 <0.10 NA <0.10 <0.10 <0.10 <0.10 <0.10 0.17 <0.10 TOC (mg/I) NA NA NA NA 17.8 NA NA NA NA NA 8.2 NA 1.6 2.8 2.1 6.7 2.4 17.2 2.7 13.6 3.4 Methane (µgd) NA NA NA NA 50.6 NA NA NA NA NA <10.0 NA <6.6 <6.6 <6.6 <6.6 <6.6 15.8 <6.6 <6.6 <6.6 Ethane (jig/1) NA NA NA NA <6.2 NA NA NA NA NA <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 Ethane (jig/1) NA NA NA NA <6.2 NA NA NA NA NA <10.0 NA <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 <6.2 16.2 Metals 601017470 a A Arsenic NA NA NA NA <10.0 NA NA NA NA NA NA <10.0 <10.0 NA <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 <10.0 Baritmr NA NA NA NA 209 NA NA NA NA NA NA 18.2 18.5 NA 41.1 28.2 21.2 52.4 37.4 84.2 42.7 Cadmimn NA NA NA NA <I.0 NA NA NA NA NA NA <LO <1.0 NA <1.0 <1.0 <1.0 <I.0 <1.0 2.3 <1.0 Chromium NA NA NA NA 79.0 NA NA NA NA NA NA <5.0 <5.0 NA 5.4 <5.0 <5.0 6.9 <5.0 11.0 6.2 Lead NA NA NA NA <5.0 NA NA NA NA NA NA <5.0 <5.0 NA 8.6 <5.0 <5.0 <5.0 <5.0 10.4 <5.0 Selenium NA NA NA NA <10.0 NA NA NA NA NA NA <10.0 <10.0 NA <10.0 <I0.0 <10.0 <10.0 <10.0 <10.0 <10.0 Silver NA NA NA NA <5.0 NA NA NA NA NA NA <5.0 <5.0 NA <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 Mercury NA NA NA NA <0.20 NA NA NA NA NA NA <0.20 <0.20 NA <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 <0.20 Metabolic Acids (meA) Acetic Acid NA NA NA NA NA NA NA NA NA NA <5.0 NA <1.8 <1.8 <0.67 <0.67 <0.67 NA NA NA NA Butyric Acid NA NA NA NA NA NA NA NA NA NA <5.0 NA <0.87 <0.87 <0.10 <0.10 <0.10 NA NA NA NA Lactic Acid NA NA NA NA NA NA NA NA NA NA <25 NA <2.3 <2.3 <2.0 <2.0 <2.0 NA NA NA NA Propionic Acid NA NA NA NA NA NA NA NA NA NA <5.0 NA <1.0 <1.0 <0.25 <0.25 <0.25 NA NA NA NA P nvic Acid I NA I NA I NA I NA I NA I NA I NA I NA I NA I NA I <10 I NA 1 <2.0 1 Q.0 1 <0.53 1 <0.53 1 <0.53 1 NA I NA I NA I NA Notes: TOC = Total Organic Carbon: DO = Dissolvrd Oxygen; NA Not Analyzed ' = Sulfide and metals samples collected on July 17, 2013. Table 7 (Page 6 of 6) D S:WAAJAaIVRojecDlWC DOT-0DT1WTd00�DonbxM0T3(M aMmAe6hWry3111h Repv[�Trblva\Tebbe\T)Ne1.A¢m. rcs161 Hari &Hickman, PC m 9aaalh Table 8 Surface Water Parameters Former ATL Site No. 2-66 Statesville, North Carolina H&H Job No. DOT-504 Surface Water Location SS-1 u stream SS-2 downstream Sampling Date Dec-12 Feb-13 A r-13 Jun-13 Oct-13 Jan-14 Ma -14 Jul-14 Nov-14 Feb-15 Dec-12 Feb-13 A r-13 Jtut-13 Oct-13 Jan-14 May- 14 Jul-14 Nov-14 Feb-15 Field Measurements Dissolved Oxygen (rngd) 10.83 10.10 9.86 6.45 8.66 9.30 9.00 9.70 9.50 8.20 10.96 10.40 10.06 6.79 9.50 10.20 9.68 10.00 9.40 8.80 Ferrous Iron (mg/1) <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 Redox(mV) 190 174 168 43 66.6 70.4 98 182 164 111 194 163 170 34 69 69 108 277 209 161 Conductivity(µS/cm) 136.4 H6.6 121.4 33.5 123.6 131.3 120.1 118.1 116.9 110.7 128.9 115.5 133.9 43.4 130.3 136.1 85.4 135.4 121.7 115.7 pH (standard traits) 7.04 7.00 7.02 6.78 7.18 7.20 7.32 6.98 7.09 7.07 7.02 6.90 6.96 7.00 7.16 7.18 7.22 6.43 6.53 6.82 Temperature (°C) 10.6 12.0 13.3 16.4 14.2 13.0 20.4 22.9 13.4 20.9 10.9 11.1 14.0 16.1 14.2 13.1 22.4 24.0 13.4 20.9 Notes: TOC = Total Organic Carbon; DO = Dissolved Oxygen; NA = Not Analyzed i = Sulfide and metals samples collected on Judy 17. 2013. Table 8 (Page 1 of 1) FYe'S.1RRAdA Pro— DOT A MGT5 SD0M0C5DOT6 StaiavD7e 66WA 2015 aepm TMI1 TW0 TbSurtas Wale Pmamelm - .-Is Hart & Hickman, PC I S T � ", V 1 L 1.1, � � I ( • 1, tv.i ry . 946 t �� i Q "Elk, NDEq` 7y� I ' i •,��, � L�- ,r— At ` i „vial t 1 3f� Le1L..,� ( �✓ TAtH rhL it•C�Q zO +� ho .: �""..�-•--o"` "i, �' _ i' � 1/ i la � \�� `�;: -�-J";'1'f�"�T� .�1 t, �t � '�� �l r _ n tt C APPROXIMATE N 0 2000 4000 SCALE IN FEET U.S.G.S. QUADRANGLE MAP STATESVILLE WEST, NC 1993 QUADRANGLE 7.5 MINUTE SERIES (TOPOGRAPHIC) t J J FORMER ATL . 46. TITLE SITE LOCATION MAP PROJECT FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA hartN hickman 2923 S Tryon Street. Suite 100 Charlotte. NC 28203 7 SMARTER ENVIRONMENTAL SOLUTIONS04 586 0007(p) 704,586 0373(f) DATE: 10-06-14 REVISION NO: 0 JOB NO: DOT-504 FIGURE NO: 1 \ LEGEND — - - — SITE PROPERTY BOUNDARY I - — - STREAM SHALLOW MONITORING WELL \ Q DEEP MONITORING WELL T MONITORING WELL BEDROCK QDMW-8 ® WATER SUPPLY WELL ASS-1 ABANDONED WATER SUPPLY ` _.._.•— I WELL — — TRIBUTARY SURFACE WATER SAMPLE TEMPORARY MONITORING WELL �✓ I I • SOIL BORING DMW-6 TREES I TREES - I DMW-10 • 1 � I I I DMW-5Q AGGEGRATE DMW-9 MAIN Q GARAGE `I I I ' liLli STOCK PILES DMW-2 FORMER ASPHALT Q •GPs TESTING LABORATORIES MW--2 1SMW-1 -2 f I TW-3 GP - / PARKING GP-2• GP-3 WSW-2 I lr AGGEGRATE STOCK PILES • wsw-1 ASTS GP-1 SMW-3® TW-g DMW-1 TW-1 I / TWS 00 DMW-4+ I AGGEGRATE STOCK O PILES I / SMW-4 ® WSW-4 WSW-4A (ACTIVE) (INACTIVE) APPROXIMATE DMW H HOPPER OFFICE I 0 100 200 AGGEGRATE I STOCK PILES SCALE IN FEET TREES _ TME SITE MAP PROA= FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA SOUTHERN RAILROAD 2923 South Tryon Street -Suite 100 hart '1• hickman Chazlotte, North Cazolina 28203 704-586-0007(p) 704-586-0373(o SNAKIER ENVIKONNEIRALSOWIWNS License # C-1269 / #C-245 Geol( DATE: 06-01-15 REVISION NO. 0 JOB NO. DOT-504 FIGURE NO. 2 I EGENf� WATER SUPPLY WELL ABANDONED WATER SUPPLY WELL --- SITE PROPERTY BOUNDARY ---- OTHER PROPERTY BOUNDARY —► ESTIMATED GROUND WATER FLOW DIRECTION NOTES: 1. MAP BASED ON RICHARD CATLIN & ASSOCIATES JUNE 1997 CSA & IREDELL COUNTY GIS DATABASE 2. WATER SUPPLY WELLS ARE KEYED TO TABLE 1 OUk� p0 W \ f R �SfMfNT FORMER ASPHALT TESTING LABORATOF WSW-1 WSW-2 I WSW-4A WSW— _J * WSW-7 / ' wsw=s wsW-8 ; i i WSW-94 i 1 / �— 1 14Ns 10 s 1 I wsWk 1 j WSW-17 SW w-l2 WSW— 1--� --- i !71 APPROXIMATE No Soo 1000 SCALE IN FEET WATER SUPPLY WELL LOCATION MAP mwrcir FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA • hart hickman 2923 South Tryon Street -Suite 100 Charlotte, North Carolina 28203 704-586-0007(p)704-586-0373(0 SNAKIER ENVIIt)NMENTAL SOLUTIONS License # C-1269 / #C-245 Geolc DATE: 06-01-15 REVISION NO. 0 JOB NO: DOT-504 FIGURE NO. 3 \ LEGEND SITE PROPERTY BOUNDARY ! — — — STREAM SHALLOW MONITORING WELL Q DEEP MONITORING WELL T MONITORING WELL BEDROCK QDMw-B ® WATER SUPPLY WELL SS-1 ....� — .. — .. — ABANDONED WATER SUPPLY _.._..�•—•._ I WELL — " TRIBUTARY SS-2 . • � ' • �� • A SURFACE WATER SAMPLE TEMPORARY MONITORING WELL I ------ ESTIMATED GROUND WATER TREES EOS INJECTION LOCATION y I LOW DIRECTION TREES ~•DMA-7 • • • • • •D w-11 3 \ TCE ISOCONCENTRATION CONTOUR (pgA) DMW-10 3 • • • • • • • I DMW-5 . DMW-9 MAIN I • GARAGE I AGGEGRATE I STOCK PILES 2 FORMER ASPHALT DMw-Q P s I TESTING LABORATORIES SMw-ple G 1SMW-1 Tw4 I • � i� j TW-2 ' TW-3�. GP- �} U PARKING / AGGEGRATE GP 2. GP 3 S WSW-2 AST S ti STOCK PILES GP-1 SMW3® TW6 -1 I DMW-1 TWA TW-5 OO / J DMW-4+ I AGGEGRATE O I ' STOCK PILES / sue 1® ,(N�(WS� ^C) ) APPROXIMATE / DMW T 0 100 200 ' HOPPER OFFICE I AGGEGRATE / - STOCK PILES I SCALE IN FEET TREES ,nE EOS INJECTION POINT LOCATIONS TREES SOUTHERN RAILROAD FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA � 2923 Suth Tryon Stteet-Sui100 hart hickman Charlotteo, North Carolina 28203te 704-586-0007(p) 704-586-0373(� SMARM OMMMiAUM SoUnIM License # C-1269 / #C-245 Geok DATE: 06-01-15 REVISION NO. 0 JOB NO. DOT-504 FIGURE NO. 4 1 DMW-8 Q (60.48) .. — • • — .. TRIBUTARY _ �r DMW-6C `j62 TREES TTDMW-7 TREES DMW-11 (61.69) DMW-10 66 (60.63) 1 68 � 70 I I I DMW-5 (NM) DMW 9(61.39) MAIN GARAGE AGGEGRATE I STOCK PILES I FORMER ASPHALT (64172Q TESTING LABO RIES •GPI SMW-2 I I SMW-1 �(63.98) +TW"2 (64.10) TW-4 I w GP I U I GP-2• [GP-3 v-WSW-2 PARKING T AGGEGRATE STOCK PILES 62GP-1• L(6s.11) SMW-3 G+ wSw-1 ASTS TW-6 I _ DMW-1 �-1 (65.26) TW-5 OO AGGEGRATE 72 DMW�� STOCK PILES 6¢ (65.19) 0 66 SMW4 68 / wsw4,e,' (ACTIVE) �w (INA %O•DMw (72.96) HOPPER � OFFICE I 172� AGGEGRATE I STOCK PILES, I TREES - I I I I i 1 7 , ,. . . . - - _ _ — TREES SOUTHERN RAILROAD LEGEND SITE PROPERTY BOUNDARY — — — STREAM SHALLOW MONITORING WELL Q DEEP MONITORING WELL + BEDROCK MONITORING WELL ® WATER SUPPLY WELL ABANDONED WATER SUPPLY WELL SURFACE WATER SAMPLE ® MONITORING WELL SHALLOW SAPROLITE TEMPORARY MONITORING WELL • SOIL BORING (63.98) SAPROLITE GROUNDWATER ELEVATION (FT) (FEBRUARY 2015) 64 GROUNDWATER POTENTIOMETRIC CONTOUR (FT) —► ESTIMATED FLOW DIRECTION NM NM NOT MEASURED B 1 1 APPROXIMATE 0 100 200 SCALE IN FEET ME ESTIMATED SHALLOW GROUNDWATER POTENTIOMETRIC MAP - FEBRUARY 2015 FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA 2923 South Tryon Street -Suite 100 had hickman Charlotte, North Catolina28203 704-586-0007(p) 704-586-0373(o SMARTS11 ENVRONMENULL SOIUiIONS license # C-1269 / #C-245 Geolc DATE: 06-01-15 REVISION NO. 0 JOB NO. DOT-504 FIGURE NO. 5 DMW-8 (DS 5/14 7/14 11/14 2/15 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 Iss2. � �- - ..-••- DMW-10 (DS) i/14 7/14 11/14 2/15 <1 <1 <1 <1 - - <1 <1 <1 <1 TREES <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 DMW1(-1(-1( AGGEGRATE STOCK PILES DMW-6 (DS) 5/14 7/14 11/14 2/15 64.9 43.2 46.7 41.8 3.1 1.9 2 1.5 67.7 52.0 59.7 55 57.2 40.6 47.5 42.3 1Q 1)S v1W-1 SS 0/13 5/14 11/14 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 DMW-1 (DS) 5/14 7/14 11/14 2/15 1.6 2.1 1.0 1.2 <1 <1 <1 <1 <1 1.3 <1 <1 2.9 4.2 2.4 2.5 2 3.5 1.9 1 2 TREES DMW-11 (DS) 5/14 7/14 11/14 2/15 6.3 7.9 9.8 1 7 <1 <1 <1 <1 7.5 11.0 13.2 9.5 5.4 8.6 10 6.7 <1.0 <1.0 <1.0 <1.0 LEGEND SITE PROPERTY BOUNDARY - - - STREAM SHALLOW MONITORING WELL Q DEEP MONITORING WELL + MONITORING WELL BEDROCK ® WATER SUPPLY WELL ABANDONED WATER SUPPLY 1 WELL I I SURFACE WATER SAMPLE TEMPORARY MONITORING WELL I ESTIMATED GROUNDWATER FLOW DIRECTION .ES I3 TCE ISOCONCENTRATION CONTOUR (NgA) '15 :1 I:1 :1 I 1 I f I I 2/15 =DATE <1=TRICHLOROETHENE (Ng/1) I <1=1,1,1-TRICHLOROETHANE (pg/1) <1 =1,1-DICHLOROETHENE (pg/1) 3.7 =1,1-DICHLOROETHANE (Ng/1) 1 1.4 =CIS-1,2-DICHLOROETHENE (pg/I) I PARKING I I 1 I I WSW-4 WSW-0A (Acme) �(INACme) APPROXIMATE )FFICE I o 100 200 SCALE IN FEET TARGET VOC CONCENTRATIONS IN SAPROLITE GROUNDWATER PROJM7 TREES I FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA SOUTHERN RAILROAD • 2923 South Tryon Street -Suite 100 hart'"` hiekman Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f SNU1RIHl ENVIROMJIQidL SOWIXW License # C-1269 / #C-245 Geolo DATE: 06-01-15 REVISION NO. 0 JOB NO. DOT-504 FIGURE NO. 6 QDMW-8 -TRIBUTARY — — � ss-z� • • � ' �— ' DMW-7 (SBR) 5/14 7/14 11/14 2/15 <1 I <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 / / DMW-6- _. DMW-11 TREES / / u LLI • U / / TREES - I— =7-,7 7,7 i i,,- -- — — SOUTHERN RAILROAD DMW-3 SBR 4/13 10/13 5/14 2/15 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 MAIN iARAGE I I TREES I I �I WSW-4 V13 5/14 11/14 2/15 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 I <1 <1 <1 TREES <1 <1 <1 OFFICE I I I 1 I I I I 4 WSW-4A 7 (INACTIVE) I I r LEGEND SITE PROPERTY BOUNDARY — — — STREAM SHALLOW MONITORING WELL Q DEEP MONITORING WELL + MONITORING WELL BEDROCK ® WATER SUPPLY WELL ABANDONED WATER SUPPLY WELL SURFACE WATER SAMPLE TEMPORARY MONITORING WELL • SOIL BORING 2/15 =DATE <1=TRICHLOROETHENE (Ng/1) <1=1,1,1—TRICHLOROETHANE (Ng/1) <1 =1,1—DICHLOROETHENE (Ng/1) <1 =1,1—DICHLOROETHANE (pg/1) <1 =CIS-1,2—DICHLOROETHENE (pg/1) APPROXIMATE 0 100 200 SCALE IN FEET TARGET VOC CONCENTRATIONS IN BEDROCK GROUNDWATER FORMER ATL SITE #2-66 STATESVILLE, NORTH CAROLINA � 2923 Suth Tryonteet-Suite hart hickman Charlottoe, North CStazolina 28203100 704-586-0007(p) 704-586-0373(f SMARM! EtMotHAENM SOWIEONS License # C-1269 / #C-245 Geok DATE: 06-01-15 REVISION NO. 0 JOB NO. DOT-504 FIGURE NO. 7 Appendix A Laboratory Analytical Data 14 hart hickman SMARTER ENVIRONMENTAL SOLUTIONS aceAnalytical www.pacelabs.com November 19, 2014 Chemical Testing Engineer NCDOT Materials & Tests Unit 1801 Blue Ridge Road Raleigh, NC 27607 RE: Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Dear Chemical Engineer: Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Enclosed are the analytical results for sample(s) received by the laboratory on November 06, 2014. The results relate only to the samples included in this report. Results reported herein conform to the most current TNI standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report. Analyses were performed at the Pace Analytical Services location indicated on the sample analyte page for analysis unless otherwise footnoted. If you have any questions concerning this report, please feel free to contact me. Sincerely, Kevin Godwin kevin.godwin@pacelabs.com Project Manager Enclosures �e pCCRF�� geORA,�pQ, REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 1 of 51 aceAnalytical j www..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 I Minnesota Certification IDs 1700 Elm Street SE Suite 200, Minneapolis, MN 55414 A&A Certification M 2926.01 Alaska Certification M UST-078 Alaska Certification #MN00064 Alabama Certification #40770 Arizona Certification #: AZ-0014 Arkansas Certification #: 88-0680 California Certification M 01155CA Colorado Certification #Pace Connecticut Certification M PH-0256 EPA Region 8 Certification M 8TMS-L Florida/NELAP Certification #: E87605 Guam Certification M14-008r Georgia Certification M 959 Georgia EPD M Pace Idaho Certification M MN00064 Hawaii Certification #MN00064 Illinois Certification M 200011 Indiana Certification#C-MN-01 Iowa Certification #: 368 Kansas Certification #: E-10167 Kentucky Dept of Envi. Protection - DW #90062 Kentucky Dept of Envi. Protection - WW #:90062 Louisiana DEQ Certification M 3086 Louisiana DHH #: LA140001 Maine Certification #: 2013011 Maryland Certification #: 322 Michigan DEPH Certification #: 9909 Charlotte Certification IDs 9800 Kincey Ave. Ste 100, Huntersville, NC 28078 North Carolina Drinking Water Certification #. 37706 North Carolina Field Services Certification M 5342 North Carolina Wastewater Certification M 12 South Carolina Certification M 99006001 Asheville Certification IDs 2225 Riverside Drive, Asheville, NC 28804 Florida/NELAP Certification #: E87648 Massachusetts Certification P. M-NC030 North Carolina Drinking Water Certification #: 37712 CERTIFICATIONS Minnesota Certification M 027-053-137 Mississippi Certification M Pace Montana Certification #: MT0092 Nevada Certification #: MN 00064 Nebraska Certification M Pace New Jersey Certification #: MN-002 New York Certification #: 11647 North Carolina Certification M 530 North Carolina State Public Health * 27700 North Dakota Certification M R-036 Ohio EPA M 4150 Ohio VAP Certification #: CL101 Oklahoma Certification M 9507 Oregon Certification #: MN200001 Oregon Certification #: MN300001 Pennsylvania Certification #: 68-00563 Puerto Rico Certification Saipan (CNMI) #:MP0003 South Carolina #:74003001 Texas Certification M T104704192 Tennessee Certification M 02818 Utah Certification M MN000642013-4 Virginia DGS Certification #. 251 Virginia/VELAP Certification #: Pace Washington Certification M C486 West Virginia Certification M 382 West Virginia DHHR *9952C Wisconsin Certification M 999407970 Florida/NELAP Certification #: E87627 Kentucky UST Certification #: 84 West Virginia Certification M 357 VirginiaNELAP Certification #: 460221 North Carolina Wastewater Certification #: 40 South Carolina Certification #: 99030001 West Virginia Certification #. 356 Virginia/VELAP Certification #: 460222 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 2 of 51 i aceAnalytical www.pacelabs.com SAMPLE ANALYTE COUNT Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 HuntersAlle, NC 28078 (704)875-9092 Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Analytes Lab ID Sample ID Method Analysts Reported Laboratory 92224577001 DMW-10 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577002 SMW-2 RSK 175 JRB 3 PASI-M EPA 6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310E AES2 1 PASI-A 92224577003 DMW-2 RSK 175 JRB 3 PASI-M EPA 6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577004 DMW-11 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577005 SMW-1 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Without the written consent of Pace Analytical Services, Inc.. Page 3 of 51 7 ci Analytical e www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 SAMPLE ANALYTE COUNT Pace Analytical Services, Inc. Kincey Ave. te 100 9800Hunte sville, NC1280778 (704)875-9092 -. jl Analytes Lab ID Sample ID Method Analysts Reported Laboratory EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577006 DMW-6 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A _ SM 6200B CAH 33 PASI-C SM 4500-S21D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577007 DMW-9 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S21) JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A — EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577008 DMW-8 RSK 175 JRB 3 PASI-M —� EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577009 SMW-3 RSK 176 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S21) JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577010 DMW-7 RSK 175 JRB 3 PASI-M i EPA6010 JMW 7 PASI-A REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, J r without the written consent of Pace Analytical Services, Inc.. Page 4 of 51 - 5acmnalytical j www..pacelabs.com f SAMPLE ANALYTE COUNT Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersviile, NC 28078 (704)875-9092 Project: Pace Project No.: DOT-504 34613.3.26 92224577 Analytes Lab ID Sample ID Method Analysts Reported Laboratory EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577011 DMW-1 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S213 JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577012 DMW-4 RSK 176 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200E CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92224577013 WSW-4 SM 6200B CAH 33 PASI-C REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 5 of 51 .0-1911 aceAnalytical 1 www.pacelabs.com i Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-10 Parameters Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577001 Collected: 11/05/14 10:45 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qua[ RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 14:40 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 14:40 74-85-1 Methane 1200 ug/L 6.6 1 11/11/14 14:40 74-82-8 6010 MET ICP Analytical Method: EPA6010 Preparation Method: EPA3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 01:46 7440-38-2 Barium 122 ug/L 5.0 1 11/07/14 15:20 11/08/14 01:46 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 01:46 7440-43-9 Chromium ND ug/L 5.0 1 11/07/1415:20 11/08/14 01:46 7440-47-3 Lead ND ug/L 5.0 1 11/07/1415:20 11/08/14 01:46 7439-92-1 Selenium ND ug/L 10.0 1 11/07/1415:20 11/08/14 01:46 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 01:46 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/0711412:00 11/07/1414:50 7439-97-6 M1 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 11/12/14 17:46 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/1417.46 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/1417.46 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 17:46 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11112/1417:46 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/1211417:46 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 17:46 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/1417A6 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/1417:46 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11112/1417:46 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 17:46 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 17:46 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 17:46 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 17:46 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 17:46 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 17:46 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 17:46 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 17:46 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 17:46 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 17:46 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 17:46 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 17:46 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 17A6 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 17:46 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 17:46 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/1417A6 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/1417A6 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 17:46 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 17:46 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 6 of 51 �- aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-10 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate I 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 6310B TOC Total Organic Carbon Date: 11/19/2014 05:39 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577001 Collected: 11/05/14 10:45 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/1417:46 106-93-4 95 % 70-130 1 11/12/1417:46 460-00-4 94 % 70-130 1 11/12/1417:46 17060-07-0 100 % 70-130 1 11/12/1417:46 2037-26-5 Analytical Method: SM 4500-S21) ND mg/L 0.10 1 11/11/1414:20 18496-25-8 Analytical Method: EPA 300.0 18.3 mg/L 2.0 1 11/09/14 02:37 14808-79-8 Analytical Method: EPA 353.2 ND mg/L 0.020 1 11/07/14 01:23 Analytical Method: SM 5310B 46.1 mg/L 1.0 1 11/08/14 21:53 7440-44-0 M1 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 7 of 51 55'cie Analytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: SMW-2 Parameters Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577002 Collected: 11/05/14 11:20 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qua[ RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 14:51 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 14:51 74-85-1 Methane 136 ug/L 6.6 1 11/11/14 14:51 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 01:56 7440-38-2 Barium 34.7 ug/L 5.0 1 11/07/14 15:20 11/08/14 01:56 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 01:56 7440-43-9 Chromium ND ug/L 5.0 1 11/07/1415:20 11/08/14 01:56 7440-47-3 Lead ND ug/L 5.0 1 11/07/1415:20 11/08/14 01:56 7439-92-1 Selenium ND ug/L 10.0 1 11/07/1415:20 11/08/14 01:56 7782-49-2 Silver ND ug/L 5.0 1 11/07/1415:20 11/08/14 01:56 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/14 14:58 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 2.2 ug/L 1.0 1 11/12/14 18:02 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/1211418:02 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 18:02 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 18:02 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 18:02 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:02 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 18:02 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 18:02 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:02 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:02 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 18:02 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 18:02 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 18:02 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 18:02 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 18:02 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 18:02 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 18:02 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 18:02 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 18:02 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 18:02 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11112/1418:02 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 18:02 75-71-8 Methylene Chloride . ND ug/L 2.0 1 11/12/14 18:02 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11112/1418:02 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 18:02 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 18:02 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/14 18:02 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/1211418:02 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 18:02 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 8 of 51 aceAnalytical mm..pacelabs.com i Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: SMW-2 i Parameters 601 Volatiles by SM 6200 1,2-Dibromoelhane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577002 Collected: 11/05/14 11:20 Results Units Report Limit DF Received: 11/06/14 15:42 Matrix: Water Prepared Analyzed CAS No. Qua[ Analytical Method: SM 6200B ND ug/L 1.0 1 11/1211418:02 106-93-4 96 % 70-130 1 11/12/14 18:02 460-00-4 99 % 70-130 1 11/12/1418:02 17060-07-0 100 % 70-130 1 11/12/1418:02 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 11/11/14 14:20 18496-25-8 Analytical Method: EPA 300.0 54.8 mg/L 4.0 2 11/12/14 11:47 14808-79-8 Analytical Method: EPA 353.2 ND mg/L 0.020 1 11/07/14 01:31 Analytical Method: SM 5310B 31.2 mg/L 1.0 1 11/08/14 22:28 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 9 of 51 _1�5a'neAnalydcal" www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-2 Parameters Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577003 Collected: 11/05/14 11:50 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 15:02 74-84-0 Ethane ND ug/L 6.2 1 11/11/14 15:02 74-85-1 Methane 42.2 ug/L 6.6 1 11/11/14 15:02 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 01:59 7440-38-2 Barium 26.3 ug/L 5.0 1 11/07/1415:20 11/08/14 01:59 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 01:59 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 01:59 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 01:59 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 01:59 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 01:59 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11107/1412:00 11/07/1415:01 7439-97-6 601 Volatiles by SM. 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 1.2 ug/L 1.0 1 11/12/14 18:19 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/14 18:19 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 18:19 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 18:19 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 18:19 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:19 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 18:19 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11112/1418:19 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:19 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 18:19 109-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 18:19 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 18:19 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 18:19 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 18:19 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1418:19 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 18:19 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 18:19 108-90-7 Chloroethane ND ug/L 1.0 1 11112/1418:19 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 18:19 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 18:19 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 18:19 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 18:19 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 18:19 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 18:19 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 18:19 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 18:19 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/14 18:19 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 18:19 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 18:19 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 10 of 51 acieAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-2 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S21) Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577003 Collected: 11/05/14 11:50 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/1418:19 106-93-4 96 % 70-130 1 11/12/1418:19 460-00-4 97 % 70-130 1 11/12/1418:19 17060-07-0 100 % 70-130 1 11/12/1418:19 2037-26-5 Analytical Method: SM 4500-S213 ND mg/L 0.10 1 11/11/1414:20 18496-25-8 Analytical Method: EPA 300.0 69.3 mg/L 8.0 4 11/12/1412:01 14808-79-8 M1 Analytical Method: EPA 353.2 2.5 mg/L 0.020 1 11/07/14 01:32 Analytical Method: SM 5310B 23.6 mg/L 1.0 1 11/08/14 22:40 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11119/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 11 of 51 Pace Analytical Services, Inc. i Kincey Ave. ® 9800Huntersvlle, NCi28 78 _ te 100 aceAnalytical www.pacelabs.com (704)875-9092 ANALYTICAL RESULTS -, Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-11 Lab ID: 92224577004 Collected: 11/05/1412:25 Received: 11/06/14 15:42 Matrix: Water j Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qua[ RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 15:13 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 15:13 74-85-1 Methane 4840 ug/L 6.6 1 11/11/14 15:13 74-82-8 6010 MET ICP Analytical Method: EPA6010 Preparation Method: EPA3010' Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:02 7440-38-2 Barium 66.1 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:02 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:02 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:02 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:02 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:02 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:02 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11107/1415:03 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 10 ug/L 1.0 1 11/12/1418:36 75-34-3 1,1-Dichloroethene 13.2 ug/L 1.0 1 11/12/1418:36 75-35-4 1,1,1-Tdchloroethane ND ug/L 1.0 1 11/12/1418:36 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/1418:36 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/1418:36 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:36 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/1418:36 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/1418:36 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:36 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:36 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 18:36 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/1418:36 74-83-9 Bromoform ND ug/L 1.0 1 11/12/1418:36 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/1418:36 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1418:36 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 18:36 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/1418:36 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/1418:36 75-00-3 Chloroform ND ug/L 1.0 1 11/12/1418:36 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 18:36 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/1211418:36 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/1418:36 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/1418:36 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/1418:36 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1418:36 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/1418:36 127-18-4 Trichloroethene 9.8 ug/L 1.0 1 11/12/1418:36 79-01-6 Tdchlorofluoromethane ND ug/L 1.0 1 11/12/1418:36 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 18:36 75-01-4 Date: 11/19/2014 05:39 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 12 of 51 aceAnalytical mvw.pecolabs.com C Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-11 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-13romofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S21) Sulfide Water c Sulfide 300.0 IC Anions 28 Days Sulfate 363.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Date: 11/19/2014 05:39 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Hunlersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224677004 Collected: 11/05/14 12:25 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/1418:36 106-93-4 96 % 70-130 1 11/12/14 18:36 460-00-4 96 % 70-130 1 11/12/1418:36 17060-07-0 100 % 70-130 1 11/12/1418:36 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 11/11/14 14:20 18496-25-8 Analytical Method: EPA 300.0 39.2 mg/L 4.0 2 11/12/14 12:42 14808-79-8 Analytical Method: EPA 353.2 ND mg/L 0.020 1 11/07/14 01:34 Analytical Method: SM 5310B 45.0 mg/L 2.0 2 11/11/1415:33 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qual Page 13 of 51 aceAnalytical www.pace/ahs.com I ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Hunlersville, NC 28078 (704)875-9092 -� � I Sample: SMW-1 Parameters Lab ID: 92224577005 Collected: 11/05/14 12:50 Results Units Report Limit DF Received: 11/06/14 15:42 Matrix: Water Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 15:24 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 15:24 74-85-1 Methane ND ug/L 6.6 1 11/11/1415:24 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/1415:20 11/08/14 02:05 7440-38-2 Barium 122 ug/L 5.0 1 11/07/1415:20 11/08/14 02:05 7440-39-3 Cadmium ND ug/L 1.0 1 11/0711415:20 11/08/14 02:05 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:05 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:05 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:05 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:05 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:06 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 11/12/1418:52 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/1418:52 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/1211418:52 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/1418:52 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/1418:52 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:52 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11112/1418:52 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/1418:52 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:52 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/1418:52 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 18:52 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/1418:52 74-83-9 Bromoform ND ug/L 1.0 1 11/12/1418:52 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/1418:52 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1418:52 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 18:52 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 18:52 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/1418:52 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 18:52 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/1418:52 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/1418:52 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/1418:52 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 18:52 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11112/1418:52 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1418:52 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 18:52 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/1418:52 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 18:52 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 18:52 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 14 of 51 aceAnalXical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: SMW-1 Parameters I 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days w Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Date: 11/19/2014 05:39 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577005 Collected: 11/05/14 12:50 Results Units Report Limit DF Received: 11/06/14 15:42 Matrix: Water Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/14 18:52 106-93-4 96 % 70-130 1 11/12/14 18:52 460-00-4 98 % 70-130 1 11/12/14 18:52 17060-07-0 100 % 70-130 1 11/12/14 18:52 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 11/11/1414:20 18496-25-8 Analytical Method: EPA 300.0 20.8 mg/L 2.0 1 11/09/14 03:59 14808-79-8 Analytical Method: EPA 353.2 2.9 mg/L 0.020 1 11/07/14 01:35 Analytical Method: SM 5310B 30.9 mg/L 1.0 1 11/08/14 23:27 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 15 of 51 1�55'cmnalyticalo www..pacelabs.com r Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-6 Parameters Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577006 Collected: 11/05/14 14:20 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane 7.0 ug/L 6.2 1 11/11/14 16:34 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 16:34 74-85-1 Methane 766 ug/L 6.6 1 11/11/14 16:34 74-82-8 6010 MET ICP Analytical Method: EPA6010 Preparation Method: EPA3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:08 7440-38-2 Barium 126 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:08 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:08 7440-43-9 Chromium ND ug/L 5.0 1 11/07/1415:20 11/08/14 02:08 7440-47-3 Lead ND ug/L 5.0 1 1110711415:20 11/08/14 02:08 7439-92-1 Selenium ND ug/L 10.0 1 11/07/1415:20 11/08/14 02:08 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:08 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:09 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 47.5 ug/L 1.0 1 11/12/14 19:09 75-34-3 1,1-Dichloroethene 59.7 ug/L 1.0 1 11/12/14 19:09 75-35-4 1,1,1-Trichloroethane 2.0 ug/L 1.0 1 11/12/14 19:09 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 19:09 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 19:09 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 19:09 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 19:09 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 19:09 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/1211419:09 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 19:09 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 19:09 75-27-4 Bromomethane ND ug/L 5.0 1 11/1211419:09 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 19:09 75-25-2 cis-1,2-Dichloroethene 3.3 ug/L 1.0 1 11/12/14 19:09 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 19:09 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 19:09 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 19:09 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 19:09 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 19:09 67-66-3 Chloromethane ND ug/L 1.0 1 11/1211419:09 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 19:09 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 .11/12/14 19:09 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 19:09 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/1211419:09 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 19:09 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 19:09 127-18-4 Trichloroethene 46.7 ug/L 1.0 1 11112/1419:09 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 19:09 75-69-4 Vinyl chloride 1.5 ug/L 1.0 1 11/12/14 19:09 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 16 of 51 - 5acieAnalydcal www.pacelabs.com i Project: DOT-504 34613.3.26 Pace Project No.: 92224577 s Sample: DIVIW-6 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310E TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577006 Collected: 11/05/14 14:20 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/1419:09 106-93-4 96 % 70-130 1 11/12/1419:09 460-00-4 97 % 70-130 1 11/12/14 19:09 17060-07-C 98 % 70-130 1 11/12/1419:09 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 11/11/1414:20 18496-25-6 Analytical Method: EPA 300.0 39.8 mg/L 4.0 2 11/09/14 03:59 14808-79-8 Analytical Method: EPA 353.2 ND mg/L 0.020 1 11/07/14 01:36 Analytical Method: SM 5310B 45.0 mg/L 1.0 1 11/08/14 23:39 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Qua[ Page 17 of 51 _ aceAnalytica( www.pacelabs.com r ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-9 Lab ID: 92224577007 Collected: 11/05/14 15:00 Received: 11/06/14 15:42 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 16:56 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 16:56 74-85-1 Methane 707 ug/L 6.6 1 11/11/14 16:56 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/1415:20 11/08/14 02:11 7440-38-2 Barium 76.0 ug/L 5.0 1 11/07/1415:20 11/08/14 02:11 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:11 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:11 7440-47-3 Lead ND ug/L 5.0 1 11/07/1415:20 11/08/14 02:11 7439-92-1 Selenium ND ug/L 10.0 1 11/07/1415:20 11/08/14 02:11 7782-49-2 Silver ND ug/L 5.0 1 11107/1415:20 11/08/14 02:11 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:17 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 2.6 ug/L 1.0 1 11/12/1419:26 75-34-3 1,1-Dichloroethene 1.6 ug/L 1.0 1 11/12/1419:26 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/1419:26 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/1419:26 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/1419:26 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/1419:26 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/1419:26 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/1419:26 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11112/1419:26 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/1419:26 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/1419:26 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/1419:26 74-83-9 Bromoform ND ug/L 1.0 1 11/12/1419:26 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/1419:26 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1419:26 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 19:26 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/1419:26 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/1419:26 75-00-3 Chloroform ND ug/L 1.0 1 11/12/1419:26 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/1419:26 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/1419:26 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/1419:26 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 19:26 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11112/1419:26 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/1419:26 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/1419:26 127-18-4 Trichloroethene 2.3 ug/L 1.0 1 11/12/1419:26 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/1419:26 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 19:26 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 18 of 51 aceAnalytical www..pacelabs.com ,I Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-9 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Hunlersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577007 Collected: 11/05/1415:00 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qua[ Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/1419:26 106-93-4 97 % 70-130 1 11/12/1419:26 460-00-4 100 % 70-130 1 11/12/1419:26 17060-07-0 100 % 70-130 1 11/12/1419:26 2037-26-5 Analytical Method: SM 4500-S21) ND mg/L 0.10 1 11/11/14 14:20 18496-25-8 Analytical Method: EPA 300.0 69.3 mg/L 4.0 2 11/09/14 04:26 14808-79-8 Analytical Method: EPA 353.2 1.4 mg/L 0.020 1 11/07/14 01:37 . Analytical Method: SM 5310B 30.6 mg/L 1.0 1 11/08/14 23:54 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 19 of 61 aceAnalytical 1 www.pacelabs.com I ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-8 Lab ID: 92224577008 Collected: 11/05/14 15:50 Received: 11/06/14 15:42 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 17:07 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 17:07 74-85-1 Methane ND ug/L 6.6 1 11/11/14 17:07 74-82-8 6010 MET ICP Analytical Method: EPA6010 Preparation Method: EPA3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:24 7440-38-2 Barium 32.3 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:24 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/1415:20 11/08/14 02:24 7440-43-9 Chromium ND ug/L 5.0 1 11/07/1415:20 11/08/14 02:24 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:24 7439-92-1 Selenium ND ug/L 10.0 1 11/07/1415:20 11/08/14 02:24 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:24 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:19 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 11/12/14 19:43 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/14 19:43 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 19:43 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/1211419:43 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 19:43 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/1211419:43 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 19:43 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 19:43 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/1211419:43 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 19:43 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 19:43 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 19:43 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 19:43 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 19:43 156-59-2 cis- 1, 3-Dichloropropene ND ug/L 1.0 1 11/12/14 19:43 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 19:43 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 19:43 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 19:43 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 19:43 67-66-3 Chloromethane ND ug/L 1.0 1 11112/1419:43 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 19:43 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 19:43 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 19:43 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11112/1419:43 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 19:43 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 19:43 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/1419:43 79-01-6 Tdchlorofluoromethane ND ug/L 1.0 1 11/12/14 19:43 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 19:43 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 20 of 51 ii aceAnaljftal rmvw.pacelabs.com i ANALYTICAL RESULTS J Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-8 Parameters Lab ID: 92224577008 Collected: 11/05/14 15:50 Results Units Report Limit DF Received: 11/06/1415:42 Matrix: Water Prepared Analyzed CAS No. 601 Volatiles by SM 6200 Analytical Method: SM 6200B - 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 11/12/14 19:43 106-93-4 Surrogates 4-Bromofluorobenzene (S) 95 % 70-130 1 11/12/14 19:43 460-00-4 1,2-Dichloroethane-d4 (S) 98 % 70-130 1 11/12/14 19:43 17060-07-0 Toluene-d8 (S) 101 % 70-130 1 11/12/14 19:43 2037-26-5 4500S213 Sulfide Water Analytical Method: SM 4500-S2D ' Sulfide ND mg/L 0.10 1 11/11/14 14:20 18496-25-8 300.0 IC Anions 28 Days Analytical Method: EPA 300.0 Sulfate 2.2 mg/L 2.0 1 11/12/14 12:55 14808-79-8 353.2 Nitrogen, N021NO3 unpres Analytical Method: EPA353.2 Nitrogen, Nitrate 0.87 mg/L 0.020 1 11/07/14 01:38 5310B TOC Analytical Method: SM 5310B Total Organic Carbon 10.8 mg/L 1.0 1 11/09/14 00:06 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full. Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Qual Page 21 of 51 IeAnalytical" J www.pacelab&com I ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 _ Huntersville, NC 28078 (704)875-9092 Sample: SMW-3 Parameters Lab ID: 92224577009 Collected: 11/06/14 08:50 Results Units Report Limit DF Received: 11/06/14 15:42 Matrix: Water Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 17:18 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 17:18 74-85-1 Methane 18.7 ug/L 6.6 1 11/11/14 17:18 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:27 7440-38-2 Barium 107 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:27 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:27 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:27 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:27 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:27 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:27 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 _11/07/1415:22 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 2.3 ug/L 1.0 1 11/12/14 20:00 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/14 20:00 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 20:00 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 20:00 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 20:00 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:00 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 20:00 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 20:00 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:00 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:00 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 20:00 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 20:00 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 20:00 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:00 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:00 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 20:00 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 20:00 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 20:00 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 20:00 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 20:00 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 20:00 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 20:00 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 20:00 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:00 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:00 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 20:00 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/14 20:00 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 20:00 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 20:00 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 22 of 51 I aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: SMW-3 ' Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates -, 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) _ 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon I Date: 11/19/2014 05:39 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577009 Collected: Analytical Analytical Analytical Analytical Analytical 11/06/14 08:50 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. ' Qual Method: SM 6200B ND ug/L 1.0 1 11/12/14 20:00 106-93-4 96 % 70-130 1 11/12/14 20:00 460-00-4 101 % 70-130 1 11/12/14 20:00 17060-07-0 100 % 70-130 1 11/12/14 20:00 2037-26-5 Method: SM 4500-S2D ND mg/L 0.10 1 11/12/1415:20 18496-25-8 Method: EPA 300.0 6.4 mg/L 2.0 1 11/12/1413:09 14808-79-8 Method: EPA 353.2 0.079 mg/L 0.020 1 11/07/14 01:45 Method: SM 5310B 28.8 mg/L 1.0 1 11/09/14 00:25 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 23 of 51 laneAnalyticalo mvw.pacelabs.com ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-7 Parameters Lab ID: 92224577010 Collected: 11/06/14 09:45 Results Units Report Limit DF Received: 11/06/14 15:42 Matrix: Water Prepared Analyzed _ CAS No. Qual RSK 176 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/1417:29 74-84-0 Ethene ND ug/L 6.2 1 11111/1417:29 74-85-1 Methane ND ug/L 6.6 1 11/11/1417:29 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:30 7440-38-2 Barium 84.2 ug/L 5.0 1 11/07/1415:20 11/08/14 02:30 7440-39-3 Cadmium 2.3 ug/L 1.0 1 11/07/14 15:20 11/08/14 02:30 7440-43-9 Chromium 11.0 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:30 7440-47-3 Lead 10.4 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:30 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:30 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:30 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:24 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 11/12/14 20:17 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/1420:17 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11112/1420:17 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 20:17 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 20:17 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:17 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 20:17 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 20:17 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:17 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:17 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 20:17 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 20:17 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 20:17 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:17 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:17 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 20:17 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 20:17 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 20:17 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 20:17 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 20:17 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 20:17 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 20:17 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 20:17 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:17 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:17 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 20:17 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/14 20:17 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 20:17 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 20:17 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 24 of 51 aceAnalyfical www.pacelabs.com I i I Project: DOT-504 34613.3.26 Pace Project No.: 92224577 ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-7 Lab ID: 92224577010 Collected: 11/06/14 09:45 Received: 11/06/14 15:42 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 11/12/14 20:17 106-93-4 Surrogates 4-Bromofluorobenzene (S) 95 % 70-130 1 11/12/14 20:17 460-00-4 1,2-Dichloroethane-d4 (S) 97 % 70-130 1 11/12/14 20:17 17060-07-0 Toluene-d8 (S) 100 % 70-130 1 11/12/14 20:17 2037-26-5 4500S2D Sulfide Water Analytical Method: SM 4500-S21) Sulfide 0.17 mg/L 0.10 1 11/12/1415:20 18496-25-8 300.0 IC Anions 28 Days Analytical Method: EPA 300.0 Sulfate 24.9 mg/L 2.0 1 11/1211413:50 14808-79-8 353.2 Nitrogen, N021NO3 unpres Analytical Method: EPA 353.2 Nitrogen, Nitrate 2.9 mg/L 0.020 1 11/07/14 01:49 5310B TOC Analytical Method: SM 531013 Total Organic Carbon 13.6 mg/L 1.0 1 11/09/14 00:38 7440-44-0 Date: 11/19/2014 05:39 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qua[ Page 25 of 51 aceAnaiXical www.pacelabs.com 1 ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-1 Parameters Lab ID: 92224577011 Collected: 11/06/14 11:30 Results Units Report Limit DF Received: 11/0611415:42 Matrix: Water Prepared Analyzed CAS No. Qual RSK 176 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 17:41 74-84-0 Ethene ND ug/L 6.2 1 11/11/14 17:41 74-85-1 Methane 10.4 ug/L 6.6 1 11/11/14 17:41 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:33 7440-38-2 Barium 54.3 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:33 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:33 7440-43-9 Chromium . ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:33 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:33 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:33 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:33 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:27 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 2.4 ug/L 1.0 1 11/12/14 20:33 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11112/1420:33 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 20:33 71-65-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11112/1420:33 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11112/1420:33 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:33 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 1111211420:33 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/1211420:33 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:33 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:33 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 20:33 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 20:33 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 20:33 75-25-2 cis-1,2-Dichloroethene 1.9 ug/L 1.0 1 11/12/14 20:33 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:33 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 20:33 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 20:33 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 20:33 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 20:33 67-66-3 Chloromethane ND ug/L 1.0 1 11/12/14 20:33 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 20:33 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 20:33 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 20:33 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:33 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:33 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 20:33 127-18-4 Trichloroethene 1.0 ug/L 1.0 1 11/12/14 20:33 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 20:33 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 20:33 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 26 of 51 i 1�5acieAnalytical www..pacelabs.com 1 Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-1 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S21) Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577011 Collected: 11/06/14 11:30 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L 1.0 1 11/12/14 20:33 106-93-4 95 % 70-130 1 11/12/14 20:33 460-00-4 100 % 70-130 1 11/12/14 20:33 17060-07-0 100 % 70-130 1 11/12/14 20:33 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 11/12/1415:20 18496-25-8 Analytical Method: EPA 300.0 4.2 mg/L 2.0 1 11/12/1414:03 14808-79-8 Analytical Method: EPA 353.2 0.041 mg/L 0.020 1 11/07/1415:40 Analytical Method: SM 5310B 17.4 mg/L 1.0 1 11/11/14 19:42 7440-44-0 M1 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 27 of 51 I�AceAnalydca( www.pacelabs.com f ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-4 Parameters Lab ID: 92224577012 Collected: 11/06/14 13:10 Results Units Report Limit DF Received: 11/06/1415:42 Matrix: Water Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 11/11/14 17:52 74-84-0 Ethene ND ug/L 6.2 1 11/11/1417:52 74-85-1 Methane 189 ug/L 6.6 1 11/11/1417:52 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:36 7440-38-2 Barium 17.3 ug/L 5.0 1 11/07/14 15:20 11/08/14 02:36 7440-39-3 Cadmium ND ug/L 1.0 1 11/07/14 15:20 11/08/14 02:36 7440-43-9 Chromium ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:36 7440-47-3 Lead ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:36 7439-92-1 Selenium ND ug/L 10.0 1 11/07/14 15:20 11/08/14 02:36 7782-49-2 Silver ND ug/L 5.0 1 11/07/14 15:20 11/08/14 02:36 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 11/07/1412:00 11/07/1415:30 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 11/12/14 20:50 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 11/12/14 20:50 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 11/12/14 20:50 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 11/12/14 20:50 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 11/12/14 20:50 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:50 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 11/12/14 20:50 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 11/12/14 20:50 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:50 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 11/12/14 20:50 106-46-7 Bromodichloromethane ND ug/L 1.0 1 11/12/14 20:50 75-27-4 Bromomethane ND ug/L 5.0 1 11/12/14 20:50 74-83-9 Bromoform ND ug/L 1.0 1 11/12/14 20:50 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:50 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:50 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 11/12/14 20:50 56-23-5 Chlorobenzene ND ug/L 1.0 1 11/12/14 20:50 108-90-7 Chloroethane ND ug/L 1.0 1 11/12/14 20:50 75-00-3 Chloroform ND ug/L 1.0 1 11/12/14 20:50 67-66-3 - Chloromethane ND ug/L 1.0 1 11/12/14 20:50 74-87-3 Dibromochloromethane ND ug/L 1.0 1 11/12/14 20:50 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 11/12/14 20:50 75-71-8 Methylene Chloride ND ug/L 2.0 1 11/12/14 20:50 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 11/12/14 20:50 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 11/12/14 20:50 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 11/12/14 20:50 127-18-4 Trichloroethene ND ug/L 1.0 1 11/12/14 20:50 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 11/12/14 20:50 75-69-4 Vinyl chloride ND ug/L 1.0 1 11/12/14 20:50 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 28 of 51 - aceAnal Yl ical 1 www..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Sample: DMW-4 Parameters i 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310E TOC Total Organic Carbon Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92224577012 Collected: Analytical Analytical Analytical Analytical Analytical 11/06/14 13:10 Received: 11/06/14 15:42 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Method: SM 6200B ND ug/L 1.0 1 11/12/14 20:50 106-93-4 96 % 70-130 1 11/12/14 20:50 460-00-4 100 % 70-130 1 11/12/14 20:50 17060-07-0 99 % 70-130 1 11/12/14 20:50 2037-26-5 Method: SM 4500-S2D 0.11 mg/L 0.10 1 11/12/1415:20 18496-25-8 Method: EPA 300.0 5.0 mg/L 2.0 1 11/12/1414:17 14808-79-8 Method: EPA 353.2 ND mg/L 0.020 1 11/07/1415:59 Method: SM 5310B 27.0 mg/L 1.0 1 11/11/14 20:15 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Qual Page 29 of 51 aceAnalytical www.pacelabs.com r ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 KinceyAve. Suite too Hunlersville, NC 28078 (704)875-9092 Sample: WSW-4 Lab ID: 92224577013 Collected: 11/06/1413:30 Received: 11/06/14 15:42 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) Date: 11/19/2014 05:39 PM Analytical Method: SM 6200B ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L 96 % 96 % 99 % 1.0 1 11/12/14 21:07 75-34-3 1.0 1 11/12/14 21:07 75-35-4 1.0 1 11/12/14 21:07 71-55-6 1.0 1 11/12/14 21:07 79-00-5 1.0 1 11/12/14 21:07 79-34-5 1.0 1 11/12/14 21:07 95-50-1 1.0 1 11/12/14 21:07 107-06-2 1.0 1 11/12/14 21:07 78-87-5 1.0 1 11/12/14 21:07 541-73-1 1.0 1 11/12/14 21:07 106-46-7 1.0 1 11/12/14 21:07 75-27-4 5.0 1 11/12/14 21:07 74-83-9 1.0 1 11/12/14 21:07 75-25-2 1.0 1 11/12/14 21:07 156-59-2 1.0 1 11/12/14 21:07 10061-01-5 1.0 1 11/12/14 21:07 56-23-5 1.0 1 11/12/14 21:07 108-90-7 1.0 1 11/12/14 21:07 75-00-3 1.0 1 11/12/14 21:07 67-66-3 1.0 1 11/12/14 21:07 74-87-3 1.0 1 11/12/14 21:07 124-48-1 1.0 1 11/12/14 21:07 75-71-8 2.0 1 11/12/14 21:07 75-09-2 1.0 1 11/12/14 21:07 156-60-5 1.0 1 11/12/14 21:07 10061-02-6 1.0 1 11/12/14 21:07 127-18-4 1.0 1 11/12/14 21:07 79-01-6 1.0 1 11/12/14 21:07 75-69-4 1.0 1 11/12/14 21:07 75-01-4 1.0 1 11/12/14 21:07 106-93-4 70-130 1 70-130 1 70-130 1 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. 11/12/14 21:07 460-00-4 11/12/14 21:07 17060-07-0 11/12/14 21:07 2037-26-5 Page 30 of 51 Pace Analytical Services, Inc. ® 9800 Kincey Ave. Suite 100 aceAnalytical Huntersville, NC 28078 www..pacelabs.com (704)875-9092 I QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: AIR/21799 Analysis Method: RSK 175 QC Batch Method: RSK 175 Analysis Description: RSK 175 AIR HEADSPACE Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012 METHOD BLANK: 1841320 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, - 92224577008,92224577009,92224577010,92224577011,92224577012 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Ethane ug/L ND 6.2 11/11/1410:26 Ethene ug/L ND 6.2 11/11/1410:26 Methane ug/L NO 6.6 11/11/1410:26 LABORATORY CONTROL SAMPLE & LCSD: 1841321 1841322 -' Spike LCS LCSD LCS LCSD % Rec Max Parameter Units Conc. Result Result % Rec % Rec Limits RPD RPD Qualifiers Ethane ug/L 114 117 106 103 93 85-115 10 20 Ethene ug/L 106 108 97.4 102 92 85-115 11 20 Methane ug/L 60.7 61.5 54.7 101 90 85-115 12 20 SAMPLE DUPLICATE: 1841323 60181936012 Dup Parameter Units Result Result RPD Qualifiers Ethane ug/L 56.0 64.2 14 Ethene ug/L <3.1 ND Methane ug/L 390 434 10 SAMPLE DUPLICATE: 1841324 92224577006 Dup Parameter Units Result Result RPD Qualifiers Ethane ug/L 7.0 7.4 6 Ethene ug/L ND ND Methane ug/L 766 859 11 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit is presented to the right or the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 31 of 51 aceAnalytical www..pacelabs.com r QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ' I QC Batch: MERP/7277 Analysis Method: EPA 7470 QC Batch Method: EPA 7470 Analysis Description: 7470 Mercury Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, -- 92224577008,92224577009,92224577010,92224577011,92224577012 METHOD BLANK: 1324927 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008, 92224577009, 92224577010, 92224577011, 92224577012 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Mercury ug/L ND 0.20 11/07/1414:45 I I LABORATORY CONTROL SAMPLE: 1324928 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Mercury ug/L 2.5 2.3 94 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1324929 1324930 _ MS MSD 92224577001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Mercury ug/L ND 2.5 2.5 1.5 1.4 61 58 75-125 5 M1 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. it Page 32 of 51 JaceAnalyticale www..pacelabs.com 1 QUALITY CONTROL DATA Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: MPRP/17298 Analysis Method: EPA 6010 — QC Batch Method: EPA3010 Analysis Description: 6010 MET Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012 METHOD BLANK: 1325309 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Arsenic ug/L ND 10.0 11/08/14 01:31 Barium ug/L ND 5.0 11/08/14 01:31 Cadmium ug/L ND 1.0 11/08/14 01:31 Chromium ug/L ND 5.0 11/08/14 01:31 Lead ug/L ND 5.0 11/08/14 01:31 Selenium ug/L ND 10.0 11/08/14 01:31 Silver ug/L ND 5.0 11/08/14 01:31 LABORATORY CONTROL SAMPLE: 1325310 Spike LCS LCS % Rec Parameter Units Cone. Result % Rec Limits Qualifiers Arsenic ug/L 500 487 97 80-120 Barium ug/L 500 496 99 80-120 Cadmium ug/L 500 493 99 80-120 Chromium ug/L 500 474 95 80-120 Lead ug/L 500 498 100 80-120 Selenium ug/L 500 509 102 80-120 Silver ug/L 250 239 96 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325311 1325313 MS MSD 92224577001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual Arsenic ug/L ND 500 500 500 498 100 100 75-125 0 Barium ug/L 122 500 500 617 618 99 99 75-125 0 Cadmium ug/L ND 500 500 494 495 99 99 75-125 0 Chromium ug/L ND 500 500 474 478 95 96 75-125 1 Lead ug/L ND 500 500 489 488 98 97 75-125 0 Selenium ug/L ND 500 500 503 506 100 101 75-125 1 Silver ug/L ND 250 250 240 242 96 97 75-125 1 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 33 of 51 aceAnalytical www.pacelabs.com f QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch: MSV/29222 Analysis Method: SM 6200B QC Batch Method: SM 6200B Analysis Description: 601 by 6200B Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008, 92224577009, 92224577010, 92224577011, 92224577012, 92224577013 METHOD BLANK: 1328260 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012,92224577013 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers 1,1,1-Trichloroethane ug/L ND 1.0 1111211417:29 1,1,2,2-Tetrachloroethane ug/L ND 1.0 11/12/14 17:29 1,1,2-Trichloroethane ug/L ND 1.0 11/12/14 17:29 1,1-Dichloroethane ug/L ND 1.0 11/12/14 17:29 1,1-Dichloroethene ug/L ND 1.0 11/12/14 17:29 1,2-Dibromoethane (EDB) ug/L ND 1.0 11/12/14 17:29 1,2-Dichlorobenzene ug/L ND 1.0 11/1211417:29 1,2-Dichloroethane ug/L ND 1.0 11112/1417:29 1,2-Dichloropropane ug/L ND 1.0 11/12/14 17:29 1,3-Dichlorobenzene ug/L ND 1.0 11112/1417:29 1,4-Dichlorobenzene ug/L ND 1.0 11112/1417:29 Bromodichloromethane ug/L ND 1.0 11/12/14 17:29 Bromoform ug/L ND 1.0 11/12/1417:29 Bromomethane ug/L ND 5.0 11/12/14 17:29 Carbon tetrachloride ug/L ND 1.0 11/12/14 17:29 Chlorobenzene ug/L ND 1.0 11/12/14 17:29 Chloroethane ug/L ND 1.0 11/12/14 17:29 Chloroform ug/L ND 1.0 11/12/14 17:29 Chloromethane ug/L ND 1.0 11/12/14 17:29 cis-1,2-Dichloroethene ug/L ND 1.0 11/1211417:29 cis-1,3-Dichloropropene ug/L ND 1.0 11/1211417:29 Dibromochloromethane ug/L ND 1.0 11/1211417:29 Dichlorodifluoromethane ug/L ND 1.0 11/12/14 17:29 Methylene Chloride ug/L ND 2.0 11/12/14 17:29 Tetrachloroethene ug/L ND 1.0 11/12/14 17:29 trans-1,2-Dichloroethene ug/L ND 1.0 11/12/14 17:29 trans-1,3-Dichloropropene ug/L ND 1.0 11/12/14 17:29 Trichloroethene ug/L ND 1.0 11/12/14 17:29 Trichlorofluoromethane ug/L ND 1.0 11/12/14 17:29 Vinyl chloride ug/L ND 1.0 11/12114 17:29 1,2-Dichloroethane-d4 (S) % 97 70-130 11/12/14 17:29 4-Bromofluorobenzene (S) % 95 70-130 11/12/14 17:29 Toluene-d8 (S) % 100 70-130 11/12/14 17:29 LABORATORY CONTROL SAMPLE: 1328261 Spike LCS LCS % Rec Parameter Units Cone. Result % Rec Limits Qualifiers 1,1,1-Trichloroethane ug/L 50 54.8 110 60-140 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 34 of 51 aceAnalyiical www.pacelabs.com _I QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 LABORATORY CONTROL SAMPLE: 1328261 Parameter Units Spike Conc. LCS Result LCS % Rec % Rec Limits 1,1,2,2-Tetrachloroethane ug/L 50 53.7 107 60-140 1,1,2-Trichloroethane ug/L 50 54.4 109 60-140 1,1-Dichloroethane ug/L 50 55.2 110 60-140 1,1-Dichloroethene ug/L 50 48.3 97 60-140 1,2-Dibromoethane (EDB) ug/L 50 56.4 113 60-140 1,2-Dichlorobenzene ug/L 50 53.3 107 60A40 1,2-Dichloroethane ug/L 50 47.5 95 60-140 1,2-Dichloropropane ug/L 50 53.8 108 60-140 1,3-Dichlorobenzene ug/L 50 54.1 108 60-140 1,4-Dichlorobenzene ug/L 50 53.0 106 60-140 Bromodichloromethane ug/L 50 51.2 102 60-140 Bromoform ug/L 50 46:2 92 60-140 Bromomethane ug/L 50 30.8 62 60-140 Carbon tetrachloride ug/L 50 58.2 116 60-140 Chlorobenzene ug/L 50 54.7 109 60-140 Chloroethane ug/L 50 43.9 88 60-140 Chloroform ug/L 50 49.8 100 60-140 Chloromethane ug/L 50 38.5 77 60-140 c7is-1,2-Dichloroethene ug/L 50 55.5 111 60-140 c7is-1,3-Dichloropropene ug/L 50 57.1 114 60-140 Dibromochloromethane ug/L 50 48.4 97 60-140 Dichlorodifluoromethane ug/L 50 38.5 77 60-140 Methylene Chloride ug/L 50 50.0 100 60-140 Tetrachloroethene ug/L 50 52.1 104 60-140 trans-1,2-Dichloroethene ug/L 50 48.7 97 60-140 trans-1,3-Dichloropropene ug/L 50 58.7 117 60-140 Trichloroethene ug/L 50 53.2 106 60-140 Trichlorofluoromethane ug/L 50 37.3 75 60-140 Vinyl chloride ug/L 50 45.6 91 60-140 1,2-Dichloroethane-d4 (S) % 92 70-130 4-Bromofluorobenzene (S) % 100 70-130 Toluene-d8 (S) % 99 70-130 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1329104 1329105 MS MSD 92224577013 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD 1,1,1-Trichloroethane ug/L ND 20 20 21.7 22.3 109 111 60-140 2 1,1,2,2-Tetrachloroethane ug/L ND 20 20 20.5 21.0 103 105 60-140 2 1,1,2-Trichloroethane ug/L ND 20 20 20.6 21.2 103 106 60-140 3 1,1-Dichloroethane ug/L ND 20 20 21.9 22.6 109 113 60-140 3 1,1-Dichloroethene ug/L ND 20 20 20.6 20.8 103 104 60-140 1 1,2-Dibromoethane (EDB) ug/L ND 20 20 20.9 21.4 105 107 60-140 2 1,2-Dichlorobenzene ug/L ND 20 20 21.1 21.3 105 107 60-140 1 1,2-Dichloroethane ug/L ND 20 20 18.4 18.8 92 94 60-140 2 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Qual Page 35 of 51 aceAnalytical www..pacelabs.com QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1329104 MS 92224577013 Spike Parameter Units Result Conc. 1,2-Dichloropropane ug/L ND 20 1,3-Dichlorobenzene ug/L ND 20 1,4-Dichlorobenzene ug/L ND 20 Bromodichloromethane ug/L ND 20 Bromoform ug/L ND 20 Bromomethane ug/L ND 20 Carbon tetrachloride ug/L ND 20 Chlorobenzene ug/L ND 20 Chloroethane ug/L ND 20 Chloroform ug/L ND 20 Chloromethane ug/L ND 20 cis-1,2-Dichloroethene ug/L ND 20 cis-1,3-Dichloropropene ug/L ND 20 Dibromochloromethane ug/L ND 20 Dichlorodifluoromethane ug/L ND 20 Methylene Chloride ug/L ND 20 Tetrachloroethene ug/L ND 20 trans-1,2-Dichloroethene ug/L ND 20 trans-1,3-Dichloropropene ug/L ND 20 Tiichloroethene ug/L ND 20 Trichlorofluoromethane ug/L ND 20 Vinyl chloride ug/L ND 20 1,2-Dichloroethane-d4 (S) % 4-Bromofluorobenzene (S) % Toluene-d8 (S) % Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 - Huntersville, NC 28078 (704)875-9092 MSD Spike Conc. 1329105 MS Result MSD Result MS % Rec MSD % Rec % Rec Limits RPD 20 20.8 20.8 104 104 60-140 0 20 21.4 22.0 107 110 60-140 2 20 21.3 21.6 106 108 60-140 2 20 18.7 19.3 93 97. 60-140 4 20 16.4 16.6 82 83 60-140 1 20 14.1 14.3 70 72 60-140 2 20 22.5 22.9 113 114 60-140 2 20 21.4 21.8 107 109 60-140 2 20 18.7 18.9 94 95 60-140 1 20 19.5 20.0 97 100 60-140 3 20 15.4 16.6 77 83 60-140 8 20 21.7 22.5 108 112 60-140 4 20 20.7 20.9 103 105 60-140 1 20 17.4 17.9 87 89 60-140 3 20 17.1 17.8 85 89 60-140 4 20 16.0 17.2 80 86 60-140 8 20 20.7 21.1 103 105 60-140 2 20 19.4 20.2 97 101 60-140 4 20 21.1 21.4 105 107 60-140 1 20 20.8 21.2 104 106 60-140 2 20 16.8 17.3 84 87 60-140 3 20 19.1 19.9 95 99 60-140 4 92 92 70-130 100 99 70-130 99 98 70-130 Qual Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 36 of 51 1�5acmnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QUALITY CONTROL DATA Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch: WET/34204 Analysis Method: SM 4500-S2D QC Batch Method: SM 4500-S2D Analysis Description: 4500S2D Sulfide Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008 METHOD BLANK: 1326942 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfide mg/L ND 0.10 11/11/1414:20 LABORATORY CONTROL SAMPLE: 1326943 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Sulfide mg/L .5 0.49 98 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1326944 1326945 MS MSD 92224134002 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qua[ Sulfide mg/L ND .5 .5 0.48 0.48 95 95 90-110 0 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1326946 MS 92224598013 Spike Parameter Units Result Conc. Sulfide mg/L ND .5 1326947 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD Qual 5 0.48 0.48 95 95 90-110 0 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result Date: 11/19/2014 05:39 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, withoutthe written consent of Pace Analytical Services, Inc.. Page 37 of 51 aceAnalytical www.pacerabs.coin QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WET/34233 Analysis Method: SM 4500-S213 QC Batch Method: SM 4500-S2D Analysis Description: 4500S2D Sulfide Water Associated Lab Samples: 92224577009, 92224577010, 92224577011, 92224577012 METHOD BLANK: 1327952 Matrix: Water Associated Lab Samples: 92224577009, 92224577010, 92224577011, 92224577012 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfide mg/L ND 0.10 11112/1416:20 Pace Analytical Services, Inc. i 9800 KinceyAve. Suite 100 _ Hunlersville, NC 28078 (704)875-9092 ti 1 ' LABORATORY CONTROL SAMPLE: 1327953 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Sulfide mg/L .5 0.52 103 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1327954 MS 92224577009 Spike Parameter Units Result Conc. Sulfide mg/L ND .5 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1327956 MS 92224598019 Spike Parameter Units Result Conc. Sulfide mg/L ND .5 1327955 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD .5 0.48 0.48 93 93 90-110 0 1327957 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD .5 0.46 0.46 92 92 90-110 0 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Qual Qual � I I ! Page 38 of 51 Pace Analytical Services, Inc. ane /i na'yrna/ 9800 uncey Ave. Suite 100 078 vli/if! !V 1 Huntersville, NC 28078 www.pacelabs.com i _ (704)875-9092 i QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WETA/20850 Analysis Method: EPA 300.0 QC Batch Method: EPA 300.0 Analysis Description: 300.0 IC Anions Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012 I. METHOD BLANK: 1325952 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010,92224577011,92224577012 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfate mg/L ND 2.0 11/08/14 23:00 LABORATORY CONTROL SAMPLE: 1325953 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Sulfate mg/L 20 18.8 94 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325954 MS MSD 92223050002 Spike Spike Parameter Units Result Conc. Conc. Sulfate mg/L 172 20 20 1325955 MS MSD MS MSD % Rec Result Result % Rec % Rec Limits RPD Qual 182 180 48 39 90-110 1 M6 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325956 1325957 MS MSD 92224577003 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Sulfate mg/L 69.3 20 20 84.7 84.8 77 78 90-110 0 M1 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 39 of 51 aceAnalytical www.pacelabs.com I QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 --; I I QC Batch: WETA/20820 Analysis Method: EPA 353.2 QC Batch Method: EPA 353.2 Analysis Description: 353.2 Nitrate + Nitrite, Unpres. Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010 METHOD BLANK: 1324737 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Nitrate mg/L ND 0.020 11/07/14 01:15 LABORATORY CONTROL SAMPLE: 1324738 Spike LCS LCS % Rec Parameter Units Cone. Result % Rec Limits Qualifiers Nitrogen, Nitrate mg/L 2.5 2.6 103 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1324739 1324740 MS MSD 92224461002 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qua[ Nitrogen, Nitrate mg/L 22.9 2.5 2.5 23.4 23.4 19 19 90-110 0 M6 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1324741 1324742 MS MSD 92224577001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qua[ Nitrogen, Nitrate mg/L ND 2.5 2.5 2.4 2.4 97 97 90-110 0 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11 /19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 40 of 51 Pace Analytical Services, Inc. ® 9800 Kincey Ave. Suite 100 acie 'nal! `ical Huntersville, NC 28078 www.pacelabs.com _ (704)875-9092 I QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WETA/20832 Analysis Method: EPA 353.2 QC Batch Method: EPA 353.2 Analysis Description: 353.2 Nitrate + Nitrite, Unpres. Associated Lab Samples: 92224577011 METHOD BLANK: 1325285 Matrix: Water Associated Lab Samples: 92224577011 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Nitrate mg/L ND 0.020 11/07/14 15:12 LABORATORY CONTROL SAMPLE: 1325286 Spike LCS LCS % Rec Parameter Units Conc.. Result % Rec Limits Qualifiers Nitrogen, Nitrate mg/L 2.5 2.5 102 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325287 1325288 MS MSD 92224526006 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Nitrogen, Nitrate mg/L 0.12 2.5 2.5 2.7 2.7 103 103 90-110 0 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325289 MS 92224526002 Spike Parameter Units Result Conc. Nitrogen, Nitrate mg/L 0.31 2.5 Qual 1325290 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD Qual 2.5 3.0 3.0 107 107 90-110 0 Results presented on this page are In the units indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 41 of 51 aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WETA/20833 QC Batch Method: EPA 353.2 Associated Lab Samples: 92224577012 METHOD BLANK: 1325298 Associated Lab Samples: 92224577012 Parameter Units Nitrogen, Nitrate mg/L QUALITY CONTROL DATA Analysis Method: EPA 353.2 Analysis Description: 353.2 Nitrate + Nitrite, Unpres. Matrix: Water Blank Reporting Result Limit Analyzed Qualifiers ND 0.020 11/07/1415:55 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 L _' Huntersville, NC 28078 (704)875-9092 I 1' 1 i i LABORATORY CONTROL SAMPLE: 1325299 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Nitrogen, Nitrate mg/L 2.5 2.5 102 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325300 1325301 MS MSD 92224577012 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qua[ Nitrogen, Nitrate mg/L ND 2.5 2.5 2.5 2.5 99 99 90-110 0 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 42 of 51 Pace Analytical Services, Inc. ® 9800 Kincey Ave. Suite 100 aceAnalyiical Huntersville, NC 28078 www.pacelabs.com _ (704)875-9092 QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WETA120849 Analysis Method: SM 5310B QC Batch Method: SM 5310B Analysis Description: 5310E TOC Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010 METHOD BLANK: 1325932 Matrix: Water Associated Lab Samples: 92224577001, 92224577002, 92224577003, 92224577004, 92224577005, 92224577006, 92224577007, 92224577008,92224577009,92224577010 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Total Organic Carbon mg/L ND 1.0 11/08/14 18*49 LABORATORY CONTROL SAMPLE: 1325933 -- Spike LCS LCS % Rec Parameter Units Cone. Result % Rec Limits Qualifiers Total Organic Carbon mg/L 25 24.6 98 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325934 1325935 MS MSD 92224273001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual Total Organic Carbon mg/L 3.8 25 25 27.7 27.5 96 95 90-110 1 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1325936 1325937 MS MSD 92224577001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual Total Organic Carbon mg/L 46.1 25 25 63.0 62.5 68 66 90-110 1 M1 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. Date: 11/19/2014 05:39 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 43 of 51 1eAnalytical" www..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92224577 QC Batch: WETA/20868 QC Batch Method: SM 5310B Associated Lab Samples: 92224577011, 92224577012 METHOD BLANK: 1327747 Associated Lab Samples: 92224577011, 92224577012 Parameter Units Total Organic Carbon mg/L LABORATORY CONTROL SAMPLE: 1327748 Parameter Units Total Organic Carbon mg/L I Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 I I ,I 1" i I I I i .. i i Qualifiers MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1327749 1327750 MS MSD 92224577011 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Total Organic Carbon mg/L 17.4 25 25 31.5 31.0 56 55 90-110 1 M1 QUALITY CONTROL DATA Analysis Method: SM 5310B Analysis Description: . 5310B TOC Matrix: Water Blank Reporting Result Limit Analyzed Qualifiers ND 1.0 11/11/14 19:17 Spike LCS Conc. Result 25 25.4 LCS % Rec % Rec Limits 102 90-110 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. I Page 44 of 51 i Pace Analytical Services, Inc. aceAnalytical ® 9800 Kincey Ave. Suite 100 _ Hunlersville, NC 28078 www.pacelabs.com (704)875-9092 I� QUALIFIERS Project: DOT-504 34613.3.26 Pace Project No.: 92224577 DEFINITIONS DF - Dilution Factor, if reported, represents the factor applied to the reported data due to changes in sample preparation, dilution of the sample aliquot, or moisture content. ND - Not Detected at or above adjusted reporting limit. J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL -Adjusted Method Detection Limit. PQL - Practical Quantitation Limit. RL - Reporting Limit. S - Surrogate - 1,2-Diphenylhydrazine (8270 listed analyte) decomposes to Azobenzene. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean -Up U - Indicates the compound was analyzed for, but not detected. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. Acid preservation may not be appropriate for 2-Chloroethylvinyl ether, Styrene, and Vinyl chloride. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TN -The NELAC Institute. LABORATORIES PASI-A Pace Analytical Services - Asheville PASI-C Pace Analytical Services - Charlotte PASI-M Pace Analytical Services - Minneapolis ANALYTE QUALIFIERS M1 Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery. M6 Matrix spike and Matrix spike duplicate recovery not evaluated against control limits due to sample dilution. Date: 11/19/2014 05:39 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 45 of 51 aceAnalytical wvnvpacelabs.com i QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Analytical Lab ID Sample ID QC Batch Method QC Batch Analytical Method Batch 92224577001 DMW-10 RSK 175 AIR/21799 92224577002 SMW-2 RSK 175 AIR/21799 92224577003 DMW-2 RSK 175 AIR/21799 92224577004 DMW-11 RSK 175 AIR/21799 92224577005 SMW-1 RSK 175 AIR/21799 92224577006 DMW-6 RSK 175 AIR/21799 92224577007 DMW-9 RSK 175 AIR/21799 92224577008 DMW-8 RSK 175 AIR/21799 92224577009 SMW-3 RSK 175 AIR/21799 92224577010 DMW-7 RSK 175 AIR/21799 92224577011 DMW-1 RSK 175 AIR/21799 92224577012 DMW-4 RSK 175 AIR/21799 92224577001 DMW-10 EPA 3010 MPRP/17298 EPA 6010 ICP/15590 92224577002 SMW-2 EPA 3010 MPRP/17298 EPA 6010 ICP/15590 92224577003 DMW-2 EPA 3010 MPRP/17298 EPA 6010 ICP/15590 92224577004 DMW-11 EPA 3010 MPRP/17298 EPA 6010 ICP/15590 92224577005 SMW-1 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224677006 DMW-6 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577007 DMW-9 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577008 DMW-8 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577009 SMW-3 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577010 DMW-7 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577011 DMW-1 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577012 DMW-4 EPA 3010 MPRP/17298 EPA6010 ICP/15590 92224577001 DMW-10 EPA7470 MERP/7277 EPA7470 MERC/6995 92224677002 SMW-2 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577003 DMW-2 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577004 DMW-11 EPA7470 MERP/7277 EPA7470 MERC/6995 92224677005 SMW-1 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577006 DMW-6 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577007 DMW-9 EPA 7470 MERP/7277 EPA 7470 MERC/6995 92224577008 DMW-8 EPA 7470 MERP/7277 EPA 7470 MERC/6995 92224577009 SMW-3 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577010 DMW-7 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577011 DMW-1 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577012 DMW-4 EPA7470 MERP/7277 EPA7470 MERC/6995 92224577001 DMW-10 SM 6200B MSV/29222 92224577002 SMW-2 SM 6200B MSV/29222 92224677003 DMW-2 SM 6200B MSV/29222 92224577004 DMW-11 SM 6200B MSV/29222 92224577005 SMW-1 SM 6200B MSV/29222 92224577006 DMW-6 SM 6200B MSV/29222 92224577007 DMW-9 SM 6200E MSV/29222 92224577008 DMW-8 SM 6200B MSV/29222 92224577009 SMW-3 SM 6200B MSV/29222 92224577010 DMW-7 SM 6200B MSV/29222 92224577011 DMW-1 SM 6200E MSV/29222 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 46 of 51 - 5acmnalydcal www.pacelabs.com Ir i Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Hunlersville, NC 28078 (704)875-9092 Project: Pace Project No.: QUALITY DOT-504 34613.3.26 92224577 CONTROL DATA CROSS REFERENCE TABLE Analytical Lab ID Sample ID QC Batch Method QC Batch Analytical Method Batch 92224577012 DMW-4 SM 6200B MSV/29222 92224577013 WSW-4 SM 6200B MSV/29222 92224577001 DMW-10 SM 4500-S2D WET/34204 92224577002 SMW-2 SM 4500-S2D WET/34204 92224577003 DMW-2 SM 4500-S2D WET/34204 92224577004 DMW-11 SM 4500-S2D WET/34204 92224677005 SMW-1 SM 4500-S2D WET/34204 92224577006 DMW-6 SM 4500-S2D WET/34204 92224577007 DMW-9 SM 4500-S2D WET/34204 92224577008 DMW-8 SM 4500-S2D WET/34204 92224577009 SMW-3 SM 4500-S2D WET/34233 92224577010 92224577011 DMW-7 DMW-1 SM 4500-S2D SM 4500-S2D WET/34233 WET/34233 92224577012 DMW-4 SM 4500-S2D WET/34233 92224577001 DMW-10 EPA 300.0 WETA120850 92224577002 SMW-2 EPA 300.0 WETA/20850 92224577003 DMW-2 EPA 300.0 WETA/20850 92224577004 DMW-11 EPA 300.0 WETA/20850 92224577006 SMW-1 EPA 300.0 WETA/20850 92224577006 DMW-6 EPA 300.0 WETA/20850 92224577007 DMW-9 EPA 300.0 WETA/20850 92224577008 DMW-8 EPA 300.0 WETA/20850 92224577009 SMW-3 EPA 300.0 WETA/20850 92224677010 DMW-7 EPA 300.0 WETA/20850 92224577011 DMW-1 EPA 300.0 WETA/20850 92224577012 DMW-4 EPA 300.0 WETA120850 92224577001 DMW-10 EPA 353.2 WETA120820 92224577002 SMW-2 EPA 353.2 WETA/20820 92224577003 DMW-2 EPA 353.2 WETA120820 92224577004 DMW-11 EPA 353.2 WETA120820 92224577005 SMW-1 EPA 353.2 WETA/20820 92224577006 DMW-6 EPA 353.2 WETA/20820 92224577007 DMW-9 EPA 353.2 WETA/20820 92224577008 DMW-8 EPA 353.2 WETA/20820 92224577009 SMW-3 EPA 353.2 WETA/20820 92224577010 DMW-7 EPA 353.2 WETA/20820 92224577011 DMW-1 EPA 353.2 WETA/20832 92224677012 DMW-4 EPA 353.2 WETA/20833 92224577001 DMW-10 SM 5310B WETA/20849 92224577002 SMW-2 SM 5310B WETA/20849 92224577003 DMW-2 SM 5310B WETA/20849 92224677004 DMW-11 SM 5310B WETA/20849 92224677005 SMW-1 SM 5310B WETA/20849 92224577006 DMW-6 SM 5310E WETA/20849 92224577007 DMW-9 SM 5310B WETA/20849 j REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 47 of 51 aceAnalytical www.pacelabs.com I QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: DOT-504 34613.3.26 Pace Project No.: 92224577 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 _ Huntersville, NC 28078 (704)875-9092 I� Analytical Lab ID Sample ID QC Batch Method QC Batch Analytical Method Batch 92224577008 DMW-8 SM 5310E WETA/20849 92224577009 SMW-3 SM 5310B WETA/20849 92224577010 DMW-7 SM 5310B WETA/20849 92224577011 DMW-1 SM 5310E WETA/20868 92224577012 DMW-4 SM 5310B WETA/20868 j } REPORT OF LABORATORY ANALYSIS i I I This report shall not be reproduced, except in full, —' Date: 11/19/2014 05:39 PM without the written consent of Pace Analytical Services, Inc.. Page 48 of 51 1 ' (1R56A1l,11y11C,?1* wn rcecer r sc;U" Page 1 of 2 Number: Issuing Authority: 103-rev.15 _Pace Huntersvillp r)nnlii% t Client Name: [4url- i� Courier: . ❑ Fed Ex ❑ UPS❑ USPS❑ Client:, Co rfiercial❑ Other Custody Seal on Cooler/Box Present: ❑ yes :: no Seals intact: El yes ❑ no I. Packing Material: a ubble V❑p ❑ Bubble Ba ffi; ❑ None ❑ Other Office Thermometer Used: IR Gun Type of Ice:�/II�V Blue None ©' aS�m les on ice, cooling g p y process has begun Temp Correction Factor T1401 No Correction':< Corrected Cooler Temp.: % •C Biological Tissue is Frozen: Yes No NIA Date and Initials of pQr�son examining Temp should be above freezing to 6°C i . Comments: contents: (iL/ UI ' 6 C� Chain of Custody Present: �. es ❑No ❑NIA 1, Chain of Custody Filled Out: C . os o ❑N►A 2. Chain of Custody Relinquished: E:fes too ❑NIA 3. 4, 5. Sampler Name & Signature on COC:Yes ❑No ❑NIA Samples Arrived within Hold Time: as No ❑N/A Short Hold Time Analysis (<72hr): .yes ❑No ❑N/A 6. Rush Turn Around Time Requested: lit es o . ❑N/A 7, Sufficient Volume: y" .,Kes No [IN All / xc $, / Correct Containers Used: e es No ❑N/A g, -Pace Containers Used:es ❑No ❑N/A Containers Intact: C9'es ❑No ❑N/A 10. Filtered volume received for Dissolved tests GvYes ❑No [3 /A 11. Sample Labels match COC: ❑No ❑NIA 12. gyres -includes date/time/ID/Analysis Matrix: , ' All containers needing preservation have been checked. 13. C es ON, ❑NIA All containers needing preservation are found to be in r ❑No compliance with EPA recommendation. es ❑NIA exceptions: VOA, coliform, TOG, 0&G, !fill-DRO (water) iP- Ye�s . Samples checked for dechlorination: -❑1No C� es1'r ❑No ❑wA 14. Headspace in VOA Vials (>6mm): QYes ©n . ❑N/A 15. Trip Blank Present: gYes ❑No 12 oft, 6, Trip Blank Custody Seals Present l,JYes ❑No ❑N/A Pace Trip Blank Lot # (if purchased): +� Client Notification/ Resolution: I! � Field Data Required? Y / N Person Contacted: ° ` t; :Date/Time: Comments/ Resolution: SCURF Review: Date: SRF Review: AisadiEE] Date: !;f. // 7Note: Whenever thscrepancy affecting North Carolina compliance samples, a copy of this form will be sent to the North C I•olina DEHNR Certification Office (i.e out of hold, Incorrect preservadv'e, out of temp, Incorrect containers) i; IV n W0#A:92224577 IIIAI�IINIV� Page 49 of 51 — ----- -- --- ---- CHAIN -OF -CUSTODY ! Analytical Request Document r/ '�eeAnalytleal The Chain -of -Custody is a LEGAL DOCUMENT. All relevant fields must be completed accurately. www.i)acelabs.com Section A Section B Section C Page: ofB ` Required Client Information: Required Projcet Information: Invoice Information: Company: • Report To: Attention: i,„1�t7 a - ! • Address: Copy To: Company Name: '' t� REGULATORY AGENCY �GLQr�� , r✓: g. �j Address: j- NPDES GROUND WATER r- DRINKING WATER UST j RCRA r OTHER Email Te/�� 3'LrlA�{-i ,�J. � �ticiClGtu,.et,L•C'-V Purchase Order No.: Paw Quote Rotaronea: - Phone: - 0 : GG-%'s Fax: Project '— Name: Paw Project Manager. Site Location STATE., /VC— Requested Due DatelTAT: � Project Number. ` 5 d 4 f f P3004CM ` � . Q, 11,(p Requested Analysis Filtered (Y/N) Section D Matrix Codes E. RoqulrodCtionl Information MATRIX I CODE o z COLLECTED Preservatives Y Drinking Water OW 8 Water WT waste Water WW COtdPOSRE COMPOSITE W b 7 Product p m Q START ENDIGRAB �' Z Soiusolid St. SAMPLE ID Ape O y w w O Vs w �` E u L� �' ��) AP (A-Z 0-9 ! r) Air AR Sample IDS MUST BE UNIQUE Tissue TS o w a a Z m N e X ua o` ` 1 Other OT O U r Z CM tJ LW O-1 a ap Orn �;, J jU% G v ECa. ~ y ¢ e N Z c5 ea m d t u ` DATE TIME GATE TIME 2 2 2 Z Z M O .Q.> �� 'S Pace Project No./ Lab I.D. 2 s ' At w �? i SD ( < 17-r 4i�G✓—f1 �XX xK s t 160 x 6 lrct•d) I I f X x x x 7 LSoo I ! I I x-, a• g S'�tty-3 tt/� i�• Esc 10�i/K�- I I t I If I 7� �V 11 �titc�—j i L --A x-)t X x <<< 12 ADDITIONAL COMMENTS R!LJDMISHEDBYIAFFILIATION DATE TIME ACCEPTED BY I AFFILIATION DATE TIME SAMPLE CONDITIONS j •�•�± •n • + r �tIEL:+:i�cPif� SAMPLER NAME AND SIGNATURE V c ^ > m 0 U z w Z PRINT Name cf SAMPLER: a m m " 0 E SIGNATURE of SAMPLE DATE Signed Important Note: By signinc this forth you are accentinn P-0, meT �n a,..... .................- _ ._.--__:__ ._ �_._ _�_____ _. .. . (MWDDrM: (Owl G 0 0 rn N CA R a F-ALL-Q-020rev.07. 15-May-2007 Face, na ical CHAIN -OF -CUSTODY / Analytical Request Document The Chain -of -Custody is a LEGAL DOCUMENT. All relevant fields must be completed accurately. Page: of 1 iection A Section B Section C v.. 2equired Client Information: Required Project Information: Invoice Information: �; 0% Attention: :ampany:. Report To•� �,�c. G�bb� f�•J �`j tddress: :�{j 3 S � ;� • ,. •.ti S-{-. s-� (oC Copy To: Company Name; REGULATORY AGENCY Address: r NPDES ROUND WATER !— DRINKING WATER t— i LIST RCRA i OTHER :mail To' , C'(.r`�IntD'iG�iG�M�QJ .0 ):tr. Purchase Order No.: Paco Quote Roferonco: 'hone: - 1 2j,2Cj—) Q-ow fa-`_ Project Name: Paco Proloet Mango,. Site Location sra7E: ��� toquostod Due DateITAT: Project s'r.�du,.�-so Number. Paw Profile 9: Requested Analysis Filtered (YIN) soction.0 Matrix Codes m RoqulrodClient Information MATRIX I CODE c g COLLECTED Preservatives r Drinking Water OW V z0 Water WT waste water ww m COMPOSITEEND w y Product P i GRAB i Z SoiVSolid SL p v) SAMPLE ID Wipe WP = �? Q W (A-Z. 0-9 / :) Air AR 0 Lu e• it.i5 Sample IDS MUST BE UNIQUE Tissue TS O w I' ZO at Z y Other OT X W c T W C G d 1 a V 0 m G 1 n O = (7 O City V A L Z t R v d 121 ~ y DATE TIME DATE TIME rn nk _ _ = Z Z M O Q Pace Project No./ Lab I. 2 3 4 5 6 7 8 9 10 11 12 ADDITIONAL COMMENTS RELINQUISHED BY I AFFILIATION DATE TIME ACCEPTED BY I AFFILIATION DATE TIME SAMPLE CONDITIONS i+4- if i(� rY s l /-r i�l L57 u CC 11-C=1 J 7 \1 ORIGINAL SAMPLER NAME AND SIGNATURE PRINT Name of SAMPLER: �UQr r� �-+,, n 0 i c a } 2 ? DATE Si ned / SIGNATURE of SAMPLER: E m ~ � 2 ° � w r, O m rn 06 E (MM/DD/YY): �(�� / / 4 n G 6 to d it 'Important Note: By signing this form you are accepting Pace's NET 30 day payment terms and agreeing to late charges of 1.5% per month for any Invoices not pall O days. F-ALL-Q-020rev.07, 15-May-2007 1�5a'cmnalytical' www.pacelabs.com February 11, 2015 Chemical Testing Engineer NCDOT Materials & Tests Unit 1801 Blue Ridge Road Raleigh, NC 27607 RE: Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Dear Chemical Engineer: Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Enclosed are the analytical results for sample(s) received by the laboratory on February 04, 2015. The results relate only to the samples included in this report. Results reported herein conform to the most current TN standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report. Analyses were performed at the Pace Analytical Services location indicated on the sample analyte page for analysis unless otherwise footnoted. If you have any questions concerning this report, please feel free to contact me. Sincerely, �J,,,-- - Kevin Godwin kevin.godwin@pacelabs.com Project Manager Enclosures �Q NCCRFO� lfge0 pS��1 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 1 of 40 aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Minnesota Certification IDs 1700 Elm Street SE Suite 200, Minneapolis, MN A2LA Certification M 2926.01 Alaska Certification #: UST-078 Alaska Certification #MN00064 Alabama Certification #40770 Arizona Certification #: AZ-0014 Arkansas Certification M 88-0680 California Certification #: 01155CA Colorado Certification #Pace Connecticut Certification ##: PH-0256 EPA Region 8 Certification M 8TMS-L Florida/NELAP Certification #: E87605 Guam Certification #:14-008r Georgia Certification #: 959 Georgia EPD #: Pace Idaho Certification #: MN00064 Hawaii Certification #MN00064 Illinois Certification #: 200011 Indiana Certification#C-MN-01 Iowa Certification #. 368 Kansas Certification #: E-10167 Kentucky Dept of Envi. Protection - DW #90062 Kentucky Dept of Envi. Protection - WW #:90062 Louisiana DEQ Certification M 3086 Louisiana DHH #: LA140001 Maine Certification #: 2013011 Maryland Certification #: 322 Michigan DEPH Certification #: 9909 CERTIFICATIONS 55414 Minnesota Certification M 027-053-137 Mississippi Certification#:.Pace Montana Certification M MT0092 Nevada Certification #: MN 00064 Nebraska Certification #: Pace New Jersey Certification #: MN-002 New York Certification M 11647 North Carolina Certification M 530 North Carolina State Public Health #: 27700 North Dakota Certification #: R-036 Ohio EPA#: 4150 Ohio VAP Certification #: CL101 Oklahoma Certification M 9507 Oregon Certification #: MN200001 Oregon Certification M MN300001 Pennsylvania Certification M 68-00563 Puerto Rico Certification Saipan (CNMI) #:MP0003 South Carolina #:74003001 Texas Certification M T104704192 Tennessee Certification #. 02818 Utah Certification M MN000642013-4 Virginia DGS Certification M 251 VirginialVELAP Certification M Pace Washington Certification M C486 West Virginia Certification M 382 West Virginia DHHR #:9952C Wisconsin Certification M 999407970 Charlotte Certification IDs 9800 Kincey Ave. Ste 100, Huntersville, NC 28078 North Carolina Drinking Water Certification #: 37706 North Carolina Field Services Certification #: 5342 North Carolina Wastewater Certification #: 12 South Carolina Certification #: 99006001 Asheville Certification IDs 2225 Riverside Drive, Asheville, NC 28804 Florida/NELAP Certification #: E87648 Massachusetts Certification #: M-NC030 North Carolina Drinking Water Certification #: 37712 Florida/NELAP Certification M E87627 Kentucky UST Certification #: 84 West Virginia Certification #: 357 VirginialVELAP Certification #: 460221 North Carolina Wastewater Certification M 40 South Carolina Certification #: 99030001 West Virginia Certification #: 356 Virginia/VELAP Certification M 460222 REPORT'OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 2 of 40 aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 - Lab ID Sample ID 92236396001 DMW-10 92236396002 DMW-6 92236396003 DMW-7 92236396004 DMW-9 92236396005 DMW-8 SAMPLE ANALYTE COUNT Method RSK 175 EPA 6010 EPA 7470 SM 6200B SM 4500-S2D EPA 300.0 EPA 353.2 SM 5310B RSK 175 EPA 6010 EPA 7470 SM 6200B SM 4500-S21) EPA 300.0 EPA 353.2 SM 5310E RSK 175 EPA 6010 EPA 7470 SM 6200B SM 4500-S2D EPA 300.0 EPA 353.2 SM 5310E RSK 175 EPA 6010 EPA 7470 SM 6200B SM 4500-S2D EPA 300.0 EPA 353.2 SM 5310B RSK 175 EPA 6010 EPA 7470 SM 6200B SM 4500-S21) REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Analysts Analytes Reported Laboratory JRB 3 PASI-M JMW 7 PASI-A HVK 1 PASI-A CAH 33 PASI-C JTJ 1 PASI-A AES2 1 PASI-A DMN 1 PASI-A AES2 1 PASI-A JRB 3 PASI-M JMW 7 PASI-A HVK 1 PASI-A CAH 33 PASI-C JTJ 1 PASI-A AES2 1 PASI-A DMN 1 PASI-A AES2 1 PASI-A JRB 3 PASI-M JMW 7 PASI-A HVK 1 PASI-A CAH 33 PASI-C JTJ 1 PASI-A AES2 1 PASI-A DMN 1 PASI-A AES2 1 PASI-A JRB 3 PASI-M JMW 7 PASI-A HVK 1 PASI-A CAH 33 PASI-C JTJ 1 PASI-A AES2 1 PASI-A DMN 1 PASI-A AES2 1 PASI-A JRB 3 PASI-M JMW 7 PASI-A HVK 1 PASI-A CAH 33 PASI-C JTJ 1 PASI-A Page 3 of 40 acmnalytical www.pacelabs.com SAMPLE ANALYTE COUNT Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Lab ID Sample ID Method Analysts Analytes Reported Laboratory EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92236396006 DMW-11 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S21D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92236396007 DMW-2 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S2D JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92236396008 DMW-1 RSK 175 JRB 3 PASI-M EPA6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S21) JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92236396009 DMW-3 RSK 175 JRB 3 PASI-M EPA 6010 JMW 7 PASI-A EPA 7470 HVK 1 PASI-A SM 6200B CAH 33 PASI-C SM 4500-S21) JTJ 1 PASI-A EPA 300.0 AES2 1 PASI-A EPA 353.2 DMN 1 PASI-A SM 5310B AES2 1 PASI-A 92236396010 WSW-4 SM 6200B CAH 33 PASI-C REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 4 of 40 i 1�5acmnalytical" r www.pacelabs.com L _ Project: DOT 504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-10 Parameters Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396001 Collected: 02/03/15 11:50 Received: 02104/1516:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qua[ RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 02/06/15 17:53 74-84-0 Ethene 33.6 ug/L 6.2 1 02/06/15 17:53 74-85-1 Methane 664 ug/L 6.6 1 02/06/15 17:53 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:43 7440-38-2 Barium 282 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:43 7440-39-3 Cadmium ND ug/L 1.0 1 02/05/15 15:45 02/06/15 02:43 7440-43-9 Chromium 45.7 ug/L 5.0 1 02/05/1515:45 02/06/15 02:43 7440-47-3 Lead 22.1 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:43 7439-92-1 Selenium ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:43 7782-49-2 Silver ND ug/L 5.0 1 02/05/15 15:45 02/06/15 02:43 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 02/06/15 12:45 02/06/15 16:40 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B - 1,1-Dichloroethane ND ug/L 1.0 1 02/11/15 09:52 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 02/11/15 09:52 75-35-4 1,1,1-Tichloroethane ND ug/L 1.0 1 02/11/15 09:52 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 02/11/15 09:52 79-00-5 - 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 02111/1509:52 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 02/11/16 09:52 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 02/11/15 09:52 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 02/11/15 09:52 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 02/11/15 09:52 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 02/11/15 09:52 106-46-7 Bromodichloromethane ND ug/L 1.0 1 02/11/15 09:52 75-27-4 Bromomethane ND ug/L 5.0 1 02/11/15 09:52 74-83-9 Bromoform ND ug/L 1.0 1 02/11/15 09:52 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 09:52 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 09:52 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 02/11115 09:52 56-23-5 Chlorobenzene ND ug/L 1.0 1 02/11/15 09:52 108-90-7 Chloroethane ND ug/L 1.0 1 02/11/15 09:52 75-00-3 Chloroform ND ug/L 1.0 1 02/11/15 09:52 67-66-3 Chloromethane ND ug/L 1.0 1 02/11/15 09:52 74-87-3 Dibromochloromethane ND ug/L 1.0 1 02/11/15 09:52 12448-1 Dichlorodifluoromethane ND ug/L 1.0 1 02/11/15 09:52 75-71-8 Methylene Chloride ND ug/L 2.0 1 02/11/15 09:52 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 09:52 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 09:52 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 02/11/15 09:52 127-18-4 Trichloroethene ND ug/L 1.0 1 02/11/15 09:52 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 02/11/15 09:52 75-69-4 Vinyl chloride ND ug/L 1.0 1 02/11/15 09:52 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 5 of 40 aceAnalytical www.pacelabs.com Project: DOT 504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-10 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310E TOC Total Organic Carbon Date: 02/11/2015 05:03 PM ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 _ Huntersville, NC 28078 (704)875-9092 -, i ;I Lab ID: 92236396001 Collected: 02/03/1511:50 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L Analytical Analytical Analytical Analytical 1.0 1 02/11/15 09:52 106-93-4 105 % 70-130 1 02/11/15 09:52 460-00-4 106 % 70-130 1 02/11/15 09:52 17060-07-0 101 % 70-130 1 02/11/15 09:52 2037-26-5 Method: SM 4500-S2D 0.25 mg/L 0.10 1 02/06/15 16:45 18496-25-8 Method: EPA 300.0 19.0 mg/L 2.0 1 02/06/15 15:09 14808-79-8 Method: EPA 353.2 ND mg/L 0.020 1 02/05/15 00:17 Method: SM 5310B 18.6 mg/L 1.0 1 02/05/15 18:33 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 6 of 40 it I 1�5aneAnalytical www.pacelabs.com Ir I Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-6 Parameters RSK 175 AIR Headspace Ethane Ethene Methane 6010 MET ICP Arsenic Barium Cadmium Chromium Lead Selenium Silver 7470 Mercury Mercury 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropene 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396002 Collected: 02/03/15 12:30 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Analytical Method: RSK 175 ND ug/L 6.2 1 02/06/15 18:00 74-84-0 61.6 ug/L 6.2 1 02/06/15 18:00 74-85-1 674 ug/L 6.6 1 02/06/15 18:00 74-82-8 Analytical Method: EPA 6010 Preparation Method: EPA 3010 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:46 7440-38-2 172 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:46 7440-39-3 ND ug/L 1.0 1 02/05/15 15:45 02/06/15 02:46 7440-43-9 20.3 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:46 7440-47-3 8.9 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:46 7439-92-1 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:46 7782-49-2 ND ug/L 5.0 1 02/05/15 15:45 02/06/15 02:46 7440-22-4 Analytical Method: EPA 7470 Preparation Method: EPA 7470 ND ug/L 0.20 1 02106/1512:45 02/0611516:43 7439-97-6 Analytical Method: SM 6200B 42.3 ug/L 1.0 1 02111/1512:25 75-34-3 55.0 ug/L 1.0 1 02/11/15 12:25 75-35-4 1.5 ug/L 1.0 1 ` 02/11/15 12:25 71-55-6 ND ug/L 1.0 1 02111/1512:25 79-00-5 ND ug/L 1.0 1 02/11/15 12:25 79-34-5 ND ug/L 1.0 1 02/11/15 12:25 95-50-1 ND ug/L 1.0 1 02/11/15 12:25 107-06-2 ND ug/L 1.0 1 02/11/15 12:25 78-87-5 ND ug/L 1.0 1 02/11/15 12:25 541-73-1 ND ug/L 1.0 1 02/11/15 12:25 106-46-7 ND ug/L 1.0 1 02/11/15 12:25 75-27-4 ND ug/L 5.0 1 02111/1512:25 74-83-9 ND ug/L 1.0 1 02/11/15 12:25 75-25-2 2.7 ug/L 1.0 1 02/11/15 12:25 156-59-2 ND ug/L 1.0 1 02/11/15 12:25 10061-01-5 ND ug/L 1.0 1 02/11/15 12:25 56-23-5 ND ug/L 1.0 1 02/11/15 12:25 108-90-7 ND ug/L 1.0 1 02/11/15 12:25 75-00-3 ND ug/L 1.0 1 02111 /15 12:25 67-66-3 ND ug/L 1.0 1 02/11/15 12:25 74-87-3 ND ug/L 1.0 1 02/11/15 12:25 124-48-1 ND ug/L 1.0 1 02/11/15 12:25 75-71-8 ND ug/L 2.0 1 02/11/15 12:25 75-09-2 ND ug/L 1.0 1 02111/1512:25 156-60-5 ND ug/L 1.0 1 02111/1512:25 10061-02-6 ND ug/L 1.0 1 02/11/15 12:25 127-18-4 41.8 ug/L 1.0 1 02/11/15 12:25 79-01-6 ND ug/L 1.0 1 02/11/15 12:25 75-69-4 ND ug/L 1.0 1 02/11/15 12:25 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qua[ Page 7 of 40 aceAnalytical www.pacelabs.00m Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-6 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 — Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396002 Collected: 02/03/15 12:30 Received: 02/04/15 16:28 Matrix: Water I Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B ND ug/L 1.0 1 02/11/1512:25 106-93-4 105 % 70-130 1 02111/1512:25 460-00-4 110 % 70-130 1 02/11/15 12:25 17060-07-0 100 % 70-130 1 02111 /15 12:25 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 02/05/15 11:00 18496-25-8 Analytical Method: EPA 300.0 45.3 mg/L 4.0 2 02/06/15 15:50 14808-79-8 Analytical Method: EPA 353.2 ND rrg/L 0.020 1 02/05/15 00:18 Analytical Method: SM 5310B 8.7 mg/L 1.0 1 02/05/15 18:44 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 8 of 40 i ! 1�5aneAnalydcal www..pacelabs.com ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-7 Parameters Lab ID: 92236396003 Collected: 02/03/15 13:10 Results Units Report Limit DF Received: 02/04/15 16:28 Matrix: Water Prepared Analyzed CAS No. Qual RSK 175 AIR Headspace Analytical Method: RSK 175 Ethane ND ug/L 6.2 1 02/06/1518:06 74-84-0 Ethene ND ug/L 6.2 1 02/06/1518:06 74-85-1 Methane ND ug/L 6.6 1 02106/1518:06 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:50 7440-38-2 Barium 42.7 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:50 7440-39-3 Cadmium ND ug/L 1.0 1 02105/1515:45 02/06/15 02:50 7440-43-9 Chromium 6.2 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:50 7440-47-3 Lead ND ug/L 5.0 1 02/05/15 15:45 02/06/15 02:50 7439-92-1 Selenium ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:50 7782-49-2 Silver ND ug/L 5.0 1 02/05/15 15:45 02/06/15 02:50 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 02/06/1512:45 02/0611516:51 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 02/11/15 10:09 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 02/11/15 10:09 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 02/11/15 10:09 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 02111/1510:09 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 02/11/15 10:09 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 02/11/15 10:09 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 02/11/15 10:09 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 02/11/15 10:09 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 02/1111510:09 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 02/11/15 10:09 106A6-7 Bromodichloromethane ND ug/L 1.0 1 02/11/15 10:09 75-274 Bromomethane ND ug/L 5.0 1 02/11/15 10:09 74-83-9 Bromoform ND ug/L 1.0 1 02/11/15 10:09 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 10:09 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 02111/1510:09 10061-01-5 Carbon tetrachloride ND uglL 1.0 1 02/11/15 10:09 56-23-5 Chlorobenzene ND ug/L 1.0 1 02/11/15 10:09 108-90-7 Chloroethane ND ug/L 1.0 1 02/11/15 10:09 75-00-3 Chloroform ND ug/L 1.0 1 02/11/15 10:09 67-66-3 Chloromethane ND ug/L 1.0 1 02/11/15 10:09 74-87-3 Dibromochloromethane ND ug/L 1.0 1 02/11/15 10:09 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 02/11/15 10:09 75-71-8 Methylene Chloride ND ug/L 2.0 1 02/11/15 10:09 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 10:09 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 02111/1510:09 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 02/11/15 10:09 127-18-4 Trichloroethene ND ug/L 1.0 1 02/11/15 10:09 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 02/11/15 10:09 75-69-4 Vinyl chloride ND ug/L 1.0 1 02/11/15 10:09 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 9 of 40 acmnalytical www..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-7 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Date: 02/11/2015 05:03 PM ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 r- Lab ID: 92236396003 Collected: 02/03/15 13:10 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit Analytical Analytical Analytical Analytical Analytical DF Prepared Analyzed CAS No. Qua[ Method: SM 6200B ND ug/L 1.0 1 02/11/15 10:09 106-93-4 104 % 70-130 1 02/11/1510:09 460-00-4 108 % 70-130 1 02111/1510:09 17060-07-0 100 % 70-130 1 02/11/1510:09 2037-26-5 Method: SM 4500-S2D ND mg/L 0.10 1 02106/1516:45 18496-25-8 Method: EPA 300.0 118 mg/L 10.0 5 02/07/15 01:34 14808-79-8 Method: EPA 353.2 0.63 mg/L 0.020 1 02/05/15 00:22 Method: SM 5310B 3.4 mg/L 1.0 1 02/05/15 18:57 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 10 of 40 laneAnalytical www..pacelabs.com ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-9 Parameters Lab ID: 92236396004 Collected: 02/03/15 13:50 Results Units Report Limit DF Received: 02/04/15 16:28 Matrix: Water Prepared Analyzed CAS No. RSK 175 AIR Headspace Analytical Method: RSK 175 - Ethane ND ug/L 6.2 1 02/06/15 18:21 74-84-0 Ethene ND ug/L 6.2 1 02/06/15 18:21 74-85-1 Methane 1010 ug/L 6.6 1 02/06/15 18:21 74-82-8 + 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 02/05/15 15:45 02/06/15 02:53 7440-38-2 Barium 896 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:53 7440-39-3 Cadmium 1.1 ug/L 1.0 1 02/05/1515:45 02/06/15 02:53 7440-43-9 Chromium 209 ug/L 5.0 1 02/05/15 15:45 02/06/15 02:53 7440-47-3 Lead 32.0 ug/L. 5.0 1 02/05/15 15:45 02/06/15 02:53 7439-92-1 Selenium 10.0 ug/L 10.0 1 02/05115 15:45 02/06/15 02:53 7782-49-2 Silver ND ug/L 5.0 1 02/05/15 15:45 02/06/15 02:53 7440-22-4 7470 Mercury Analytical Method: EPA7470 Preparation Method: EPA7470 Mercury 0.47 ug/L 0.20 1 02/06/15 12:45 02/06/15 16:54 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane 3.0 ug/L 1.0 1 02/11/15 10:26 75-34-3 1,1-Dichloroethene 1.5 ug/L 1.0 1 02/11/15 10:26 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 02/11/15 10:26 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 02/1111510:26 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 02/11/15 10:26 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 02/11/15 10:26 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 02/11/15 10:26 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 02/11/15 10:26 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 02/11/15 10:26 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 02/1111510:26 106A6-7 Bromodichloromethane ND ug/L 1.0 1 02/11/15 10:26 75-27A Bromomethane ND ug/L 5.0 1 02/11/15 10:26 74-83-9 Bromoform ND ug/L 1.0 1 02/11/15 10:26 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 10:26 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 10:26 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 02/11/15 10:26 56-23-5 Chlorobenzene ND ug/L 1.0 1 02/11/15 10:26 108-90-7 Chloroethane ND ug/L 1.0 1 02/11/15 10:26 75-00-3 Chloroform ND ug/L 1.0 1 02/11/15 10:26 67-66-3 Chloromethane ND ug/L 1.0 1 02111/1510:26 74-87-3 Dibromochloromethane ND ug/L 1.0 1 02/11/15 10:26 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 02/11/15 10:26 75-71-8 Methylene Chloride ND ug/L 2.0 1 02/11/15 10:26 75-09-2 _ trans-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 10:26 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 10:26 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 02/11/15 10:26 127-18-4 Trichloroethene 2.2 ug/L 1.0 1 02111/1510:26 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 02/11/15 10:26 75-69-4 Vinyl chloride ND ug/L 1.0 1 02/11/15 10:26 75-01-4 Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qual Page 11 of 40 5ac ie A na ly Acal t www.pacelabs.com I ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 - Sample: DMW-9 Parameters Lab ID: 92236396004 Collected: 02/03/1513:50 Results Units Report Limit DF Received: 02/04/15 16:28 Matrix: Water Prepared Analyzed CAS No. Qual 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 02/11/15 10:26 106-93-4 Surrogates 4-Bromofluorobenzene (S) 105 % 70-130 1 02/11/15 10:26 460-00-4 1,2-Dichloroethane-d4 (S) 110 % 70-130 1 02/11/15 10:26 17060-07-0 Toluene-d8 (S) 101 % 70-130 1 02/11/15 10:26 2037-26-5 4500S21) Sulfide Water Analytical Method: SM 4500-S213 Sulfide ND mg/L 0.20 2 02/06/15 16:45 18496-25-8 300.0 IC Anions 28 Days Analytical Method: EPA 300.0 Sulfate 71.9 mg/L 4.0 2 02/06/15 16:17 14808-79-8 353.2 Nitrogen, NO2/NO3 unpres Analytical Method: EPA 353.2 Nitrogen, Nitrate 1.4 mg/L 0.020 1 02/05/15 00:24 5310B TOC Analytical Method: SM 5310B Total Organic Carbon 3.2 mg/L 1.0 1 02/05/15 19:07 7440-44-0 Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. I i Page 12 of 40 1�5acieAnalytical r www.pacelabs.com i Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-8 Parameters RSK 175 AIR Headspace Ethane Ethene Methane 6010 MET ICP Arsenic Barium Cadmium Chromium Lead Selenium Silver 7470 Mercury Mercury 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform c7is-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Hunlersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396005 Collected: 02/03/15 14:40 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Analytical Method: RSK 175 ND ug/L 6.2 1 02/06/1518:30 74-84-0 ND ug/L 6.2 1 02/06/15 18:30 74-85-1 ND ug/L 6.6 1 02/06/1518:30 74-82-8 Analytical Method: EPA 6010 Preparation Method: EPA 3010 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:05 7440-38-2 846 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:05 7440-39-3 ND ug/L 1.0 1 02/05/15 15:45 02/06/15 03:05 7440-43-9 81.2 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:05 7440-47-3 14.6 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:05 7439-92-1 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:05 7782-49-2 ND ug/L 5.0 1 02/05/15 15:45 02/06/15 03:05 7440-22-4 Analytical Method: EPA7470 Preparation Method: EPA7470 ND ug/L 0.20 1 02/06/1512:45 02/06/1516:56 7439-97-6 Analytical Method: SM 6200B ND ug/L 1.0 1 02/11/15 10:43 75-34-3 ND ug/L 1.0 1 02/11/15 10:43 75-35-4 ND ug/L 1.0 1 02/11/15 10:43 71-55-6 ND ug/L 1.0 1 02111/1510:43 79-00-5 ND ug/L 1.0 1 02111/1510:43 79-34-5 ND ug/L 1.0 1 02/11/15 10:43 95-50-1 ND ug/L 1.0 1 02/11/15 10:43 107-06-2 ND ug/L 1.0 1 02/11/15 10:43 78-87-5 ND ug/L 1.0 1 02/11/15 10:43 541-73-1 ND ug/L 1.0 1 02/11/15 10:43 106-46-7 ND ug/L 1.0 1 02111/1510:43 75-27-4 ND ug/L 5.0 1 0211111510:43 74-83-9 ND ug/L 1.0 1 02111/1510:43 75-25-2 ND ug/L 1.0 1 02111/1510:43 156-59-2 ND ug/L 1.0 1 02/11/15 10:43 10061-01-5 ND ug/L 1.0 1 02111/1510:43 56-23-5 ND ug/L 1.0 1 02/11/15 10:43 108-90-7 ND ug/L 1.0 1 02/11/15 10:43 75-00-3 ND ug/L 1.0 1 02/11/15 10:43 67-66-3 ND ug/L 1.0 1 02/11/15 10:43 74-87-3 ND ug/L 1.0 1 02/11/15 10:43 124-48-1 ND ug/L 1.0 1 02/11/15 10:43 75-71-8 ND ug/L 2.0 1 02/11/15 10:43 75-09-2 ND ug/L 1.0 1 02/11/15 10:43 156-60-5 ND ug/L 1.0 1 02/11/15 10:43 10061-02-6 ND ug/L 1.0 1 02/11/15 10:43 127-18-4 ND ug/L 1.0 1 02/11/15 10:43 79-01-6 ND ug/L 1.0 1 02/11/15 10:43 75-69-4 ND ug/L 1.0 1 02/11/15 10:43 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qual Page 13 of 40 - 7;a'neAnalyticalo www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 _ i. Sample: DMW-8 Lab ID: 92236396006 Collected: 02/03/15 14:40 Received: 02/04/15 16:28 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 601 Volatiles by SM 6200 Analytical Method: SM 6200B ANALYTICAL RESULTS 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 02/11/15 10:43 106-93-4 Surrogates 4-Bromofluorobenzene (S) 103 % 70-130 1 02/11/15 10:43 460-00-4 1,2-Dichloroethane-d4 (S) 108 % 70-130 1 02/11/15 10:43 17060-07-C Toluene-d8 (S) 101 % 70-130 1 02/11/15 10:43 2037-26-5 4500S2D Sulfide Water Analytical Method: SM 4500-S213 Sulfide 0.20 mg/L 0.10 1 02/05/15 11:00 18496-25-E 300.0 IC Anions 28 Days Analytical Method: EPA 300.0 Sulfate 27.0 mg/L 2.0 1 02/06/15 16:31 14808-79-6 353.2 Nitrogen, NO2/NO3 unpres Analytical Method: EPA353.2 Nitrogen, Nitrate 0.81 mg/L 0.020 1 02/05/15 00:25 5310B TOC Analytical Method: SM 5310B Total Organic Carbon 20.6 mg/L 1.0 1 02/05/15 19:33 7440-44-0 Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 14 of 40 aceAnalytical www..pacelabs.com Project: DOT 504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-11 Parameters RSK 175 AIR Headspace Ethane Ethene Methane 6010 MET ICP Arsenic Barium Cadmium Chromium Lead Selenium Silver 7470 Mercury Mercury 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396006 Collected: 02/03/15 16:20 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: RSK 175 ND ug/L 6.2 1 02/06/15 18:38 74-84-0 ND ug/L 6.2 1 02/06/15 18:38 74-85-1 4560 ug/L 6.6 1 02/06/15 18:38 74-82-8 Analytical Method: EPA 6010 Preparation Method: EPA 3010 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:08 7440-38-2 789 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:08 7440-39-3 ND ug/L 1.0 1 02/05/15 15:45 02/06/15 03:08 7440-43-9 85.0 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:08 7440-47-3 .110 ug/L 5.0 1 02/05/15 15:45 .02/06/15 03:08 7439-92-1 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:08 7782-49-2 5.9 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:08 7440-22-4 Analytical Method: EPA 7470 Preparation Method: EPA 7470 ND ug/L 0.20 1 02/06/15 12:45 02/06/15 16:59 7439-97-6 Analytical Method: SM 6200B 6.7 ug/L 1.0 1 02/11/15 11:00 75-34-3 9.5 ug/L 1.0 1 02111/1511:00 75-35-4 ND ug/L 1.0 1 02/11/1511:00 71-55-6 ND ug/L 1.0 1 02/11/1511:00 79-00-5 ND ug/L 1.0 1 02/11/1511:00 79-34-5 ND ug/L 1.0 1 02/11/1511:00 95-50-1 ND ug/L 1.0 1 02/11/1511:00 107-06-2 ND ug/L 1.0 1 02111/1511:00 78-87-5 ND ug/L 1.0 1 02/11/1511:00 541-73-1 ND ug/L 1.0 1 02/11/1511:00 106-46-7 ND ug/L 1.0 1 02111/1511:00 75-27-4 ND ug/L 5.0 1 02/11/1511:00 74-83-9 ND ug/L 1.0 1 02/11/1511:00 75-25-2 ND ug/L 1.0 1 02/11/1511:00 156-59-2 ND ug/L 1.0 1 02/11/1511:00 10061-01-5 ND ug/L 1.0 1 02/11/1511:00 56-23-5 ND ug/L 1.0 1 02/11/1511:00 108-90-7 ND ug/L 1.0 1 02/11/1511:00 75-00-3 ND ug/L 1.0 1 02/11/1511:00 67-66-3 ND ug/L 1.0 1 02/11/1511:00 74-87-3 ND ug/L 1.0 1 02/11/1511:00 124-48-1 ND ug/L 1.0 1 02/11/1511:00 75-71-8 ND ug/L 2.0 1 02/11/1511:00 75-09-2 ND ug/L 1.0 1 02/11/1511:00 156-60-5 ND ug/L 1.0 1 02/11/1511:00 10061-02-6 ND ug/L 1.0 1 02/11/1511:00 127-18-4 7.0 ug/L 1.0 1 02/11/1511:00 79-01-6 ND ug/L 1.0 1 02/11/1511:00 75-69-4 ND ug/L 1.0 1 02/11/1511:00 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 15 of 40 aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-11 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofiuorobenzene (S) 1,2-Dichloroethane-d4 (S) . Toluene-d8 (S) 4500S21) Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, NO2/NO3 unpres Nitrogen, Nitrate 5310B TOC Total Organic Carbon Date: 02/11/2015 05:03 PM ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Lab ID: 92236396006 Collected: 02/03/15 16:20 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit Analytical Analytical Analytical Analytical Analytical DF Prepared Analyzed CAS No. Qual Method: SM 6200B ND ug/L 1.0 1 02111/1511:00 106-93-4 102 % 70-130 1 02/11/1511:00 460-00-4 106 % 70-130 1 02111/1511:00 17060-07-0 101 % 70-130 1 02/11/1511:00 2037-26-5 Method: SM 4500-S2D 0.14 mg/L 0.10 1 02/06/15 16:45 18496-25-8 Method: EPA 300.0 79.6 mg/L 8.0 4 02/07/15 01:48 14808-79-8 Method: EPA 353.2 ND mg/L 0.020 1 02/05/15 00:26 Method: SM 5310B 20.9 mg/L 1.0 1 02/05/15 19:44 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 16 of 40 �5acieAnalytical www.pacelabs.com Project: DOT 504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-2 Parameters RSK 175 AIR Headspace Ethane Ethene Methane 6010 MET ICP Arsenic Barium Cadmium Chromium Lead Selenium Silver 7470 Mercury Mercury 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichlo roeth ane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396007 Collected: 02/04/15 11:50 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Analytical Method: RSK 175 ND ug/L 6.2 1 02106/1519:19 74-84-0 ND ug/L 6.2 1 02/06/15 19:19 74-85-1 58.7 ug/L 6.6 1 02/06/15 19:19 74-82-8 Analytical Method: EPA6010 Preparation Method: EPA3010 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:11 7440-38-2 91.0 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:11 7440-39-3 ND ug/L 1.0 1 02/05/15 15:45 02/06/15 03:11 7440-43-9 21.2 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:11 7440-47-3 5.8 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:11 7439-92-1 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:11 7782-49-2 ND ug/L 5.0 1 02/05/15 15:45 02/06/15 03:11 7440-22-4 Analytical Method: EPA 7470 Preparation Method: EPA 7470 ND ug/L 0.20 1 02/06/15 12:45 02/06/15 17:01 7439-97-6 Analytical Method: SM 6200B 1.0 ug/L 1.0 1 02/11/1511:16 75-34-3 ND ug/L 1.0 1 02/11/1511:16 75-35-4 ND ug/L 1.0 1 02111/1511:16 71-55-6 ND ug/L 1.0 1 02/11/1511:16 79-00-5 ND ug/L 1.0 1 02/11/1511:16 79-34-5 ND ug/L 1.0 1 02/11/1511:16 95-50-1 ND ug/L 1.0 1 02/11/1511:16 107-06-2 ND ug/L 1.0 1 02/11/1511:16 78-87-5 ND ug/L 1.0 1 02/11/1511:16 541-73-1 ND ug/L 1.0 1 02/11/1511:16 106-46-7 ND ug/L 1.0 1 02/11/1511:16 75-27-4 ND ug/L 5.0 1 02/11/1511:16 74-83-9 ND ug/L 1.0 1 02/11/1511:16 75-25-2 ND ug/L 1.0 1 02/11/1511:16 156-59-2 ND ug/L 1.0 1 02/11/1511:16 10061-01-5 ND ug/L 1.0 1 02/11/1511:16 56-23-5 ND ug/L 1.0 1 02/11/1511:16 108-90-7 ND ug/L 1.0 1 02/11/1511:16 75-00-3 ND ug/L 1.0 1 02/11/1511:16 67-66-3 ND ug/L 1.0 1 02/11/1511:16 74-87-3 ND ug/L 1.0 1 02/11/1511:16 124-48-1 ND ug/L 1.0 1 02/11/1511:16 75-71-8 ND ug/L 2.0 1 02/11/1511:16 75-09-2 ND ug/L 1.0 1 02111/1511:16 156-60-5 ND ug/L 1.0 1 02/11/1511:16 10061-02-6 ND ug/L 1.0 1 - 02/11/15 11:16 127-18-4 ND ug/L 1.0 1 02/11/1511:16 79-01-6 ND ug/L 1.0 1 02/11/1511:16 75-69-4 ND ug/L 1.0 1 02/11/15 11:16 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qual Page 17 of 40 aceAnalytical f vAmpacelabs.com I Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-2 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310E TOC Total Organic Carbon Date: 02/11/2015 05:03 PM ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 1-7 Lab ID: 92236396007 Collected: 02/04/15 11:50 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B I i ND ug/L 1.0 1 02/11/15 11:16 106-93-4 102 % 70-130 1 02/11/1511:16 460-00-4 107 % 70-130 1 02111/1511:16 17060-07-0 101 % 70-130 1 02/11/1511:16 2037-26-5 Analytical Method: SM 4500-S2D ND mg/L 0.10 1 02/05/15 11:00 18496-25-8 Analytical Method: EPA 300.0 77.2 mg/L 4.0 2 02/10/15 14:06 14808-79-8 Analytical Method: EPA 353.2 2.7 mg/L 0.020 1 02/05/15 00:28 Analytical Method: SM 5310B 3.6 mg/L 1.0 1 02/05/15 19:54 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 18 of 40 aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-1 Parameters RSK 175 AIR Headspace Ethane Ethene i Methane 6010 MET ICP Arsenic Barium Cadmium Chromium Lead Selenium Silver 7470 Mercury Mercury 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trchloroethene Trichlorofluoromethane Vinyl chloride Date: 02/11/2015 05:03 PM Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Lab ID: 92236396008 Collected: 02/04/1512:50 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit DF Prepared Analyzed CAS No. Qual Analytical Method: RSK 175 ND ug/L 6.2 1 02/06/15 19:28 74-84-0 ND ug/L 6.2 1 02/06/15 19:28 74-85-1 13.8 ug/L 6.6 1 02/06/15 19:28 74-82-8 Analytical Method: EPA6010 Preparation Method: EPA3010 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:14 7440-38-2 502 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:14 7440-39-3 1.2 ug/L 1.0 1 02/05/15 15:45 02/06/15 03:14 7440-43-9 86.4 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:14 7440-47-3 27.9 ug/L 5.0 1 02/05/15 15:45 02/06/15 03:14 7439-92-1 ND ug/L 10.0 1 02/05/15 15:45 02/06/15 03:14 7782-49-2 ND ug/L 5.0 1 02/05/15 15:45 02/06/15 03:14 7440-22-4 Analytical Method: EPA7470 Preparation Method: EPA7470 ND ug/L 0.20 1 02/06/1512:45 02/06/1517:04 7439-97-6 Analytical Method: SM 6200B 2.6 ug/L 1.0 1 02/11/1511:33 75-34-3 ND ug/L 1.0 1 02/11/1511:33 75-35-4 ND ug/L 1.0 1 02/11/1511:33 71-55-6 ND ug/L 1.0 1 02/11/15 11:33 79-00-5 ND ug/L 1.0 1 02/11/1511:33 79-34-5 ND ug/L 1.0 1 02/11/1511:33 95-50-1 ND ug/L 1.0 1 02/11/1511:33 107-06-2 ND ug/L 1.0 1 02/11/1511:33 78-87-5 ND ug/L 1.0 1 02/11/1511:33 541-73-1 ND ug/L 1.0 1 02/11/1511:33 106-46-7 ND ug/L 1.0 1 02/11/1511:33 75-27-4 ND ug/L 5.0 1 02/1111511:33 74-83-9 .ND ug/L 1.0 1 02/11/1511:33 75-25-2 2.0 ug/L 1.0 1 02/11/1511:33 156-59-2 ND ug/L 1.0 1 02/11/1511:33 10061-01-5 ND ug/L 1.0 1 02/11/1511:33 56-23-5 ND ug/L 1.0 1 02/11/1511:33 108-90-7 ND ug/L 1.0 1 02111/1511:33 75-00-3 ND ug/L 1.0 1 02/11/1511:33 67-66-3 ND ug/L 1.0 1 02111/1511:33 74-87-3 ND ug/L 1.0 1 02/11/1511:33 124A8-1 ND ug/L 1.0 1 02/11/1511:33 75-71-8 ND ug/L 2.0 1 02111/1511:33 75-09-2 ND ug/L 1.0 1 02/11/1511:33 156-60-5 ND ug/L 1.0 1 02/1111511:33 10061-02-6 ND ug/L 1.0 1 02/11/1511:33 127-18-4 1.2 ug/L 1.0 1 02/11/1511:33 79-01-6 ND ug/L 1.0 1 02/11/1511:33 75-69-4 ND ug/L 1.0 1 02/11/1511:33 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 19 of 40 acmnalytical www..pacelabs.com ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 i i Sample: DMW-1 Lab ID: 92236396008 Collected: 02104/1512:50 Received: 02/04/16 16:28 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 02/11/15 11:33 106-93-4 Surrogates 4-Bromofluorobenzene (S) 101 % 70-130 1 02/11/15 11:33 460-00-4 I 1,2-Dichloroethane-d4 (S) 106 % 70-130 1 02/11/15 11:33 17060-07-0 Toluene-d8 (S) 101 % 70-130 1 02/11/15 11:33 2037-26-5 4500S2D Sulfide Water Analytical Method: SM 4500-S213 — Sulfide ND mg/L 0.10 1 02/06/15 16:45 18496-25-8 1 300.0 IC Anions 28 Days Analytical Method: EPA 300.0 Sulfate 4.3 mg/L 2.0 1 02/10/1514:23 14808-79-8 353.2 Nitrogen, N021NO3 unpres Analytical Method: EPA 353.2 Nitrogen, Nitrate 0.059 mg/L 0.020 1 02/05/15 00:29 5310E TOC Analytical Method: SM 5310B Total Organic Carbon 4.2 mg/L 1.0 1 02/05/15 20:46 7440-44-0 Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 20 of 40 1�;aceAnalytical www..pacelabs.com ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: DMW-3 Parameters Lab ID: 92236396009 Collected: 02/04/15 15:00 Results Units Report Limit DF Received: 02/04/15 16:28 Matrix: Water Prepared Analyzed CAS No. RSK 175 AIR Headspace Analytical Method: RSK 175 --- Ethane ND ug/L 6.2 1 02/06/15 19:36 74-84-0 Ethene ND ug/L 6.2 1 02/06/15 19:36 74-85-1 Methane 50.6 ug/L 6.6 1 02/06/15 19:36 74-82-8 6010 MET ICP Analytical Method: EPA 6010 Preparation Method: EPA 3010 Arsenic ND ug/L 10.0 1 02106/1510:05 02/06/15 18:32 7440-38-2 Barium 209 ug/L 5.0 1 02/06/15 10:05 02/06/15 18:32 7440-39-3 Cadmium ND ug/L 1.0 1 02/0611510:05 02/06/15 18:32 7440-43-9 Chromium 79.0 ug/L 5.0 1 02/06/15 10:05 02/06/15 18:32 7440-47-3 Lead ND ug/L 5.0 1 02/06/15 10:05 02/06/15 18:32 7439-92-1 Selenium ND ug/L 10.0 1 02/06/15 10:05 02106/1518:32 7782-49-2 Silver ND ug/L 5.0 1 02/06/15 10:05 02106/1518:32 7440-22-4 7470 Mercury Analytical Method: EPA 7470 Preparation Method: EPA 7470 Mercury ND ug/L 0.20 1 02/06/1512:45 02/06/1517:07 7439-97-6 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 02/11/15 11:50 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 02/11/15 11:50 75-35-4 1,1,1-Trichloroethane ND ug/L 1.0 1 02/11/15 11:50 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 02/11/15 11:50 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 02/11/15 11:50 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 02/1111511:50 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 02/11/15 11:50 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 02/11/15 11:50 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 02/11/15 11:50 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 02/11/15 11:50 106-46-7 Bromodichloromethane ND ug/L 1.0 1 02/11/15 11:50 75-27-4 Bromomethane ND ug/L 5.0 1 02/11/15 11:50 74-83-9 Bromoform ND ug/L 1.0 1 02/11/1511:60 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 11:50 156-59-2 - cis-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 11:50 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 02/11/15 11:50 56-23-5 Chlorobenzene ND ug/L 1.0 1 02/11/15 11:50 108-90-7 Chloroethane ND ug/L 1.0 1 02/11/15 11:50 75-00-3 Chloroform ND ug/L 1.0 1 02/1111511:50 67-66-3 Chloromelhane ND ug/L 1.0 1 02111/1511:50 74-87-3 Dibromochloromethane ND ug/L 1.0 1 02/11/15 11:50 124-48-1 Dichlorodifluoromethane ND ug/L 1.0 1 02/11/15 11:50 75-71-8 Methylene Chloride ND ug/L 2.0 1 02/11/15 11:50 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 02111/1511:50 156-60-5 r trans-1,3-Dichloropropene ND ug/L 1.0 1 02111/1511:50 10061-02-6 Tetrachloroethene ND uglL 1.0 1 02/11/15 11:50 127-18-4 Trichloroethene ND uglL 1.0 1 02/11/15 11:50 79-01-6 Trichlorofluoromethane ND ug/L 1.0 1 02/11/15 11:50 75-69-4 j Vinyl chloride ND ug/L 1.0 1 02/11/15 11:50 75-01-4 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Qual Page 21 of 40 1�5a'cieAnalytica( ( www.pacelabs.com I Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Sample: DMW-3 Parameters 601 Volatiles by SM 6200 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) 4500S2D Sulfide Water Sulfide 300.0 IC Anions 28 Days Sulfate 353.2 Nitrogen, N021NO3 unpres Nitrogen, Nitrate 5310E TOC Total Organic Carbon Date: 02/11/2015 05:03 PM ANALYTICAL RESULTS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 �1 �I Lab ID: 92236396009 Collected: 02/04/1515:00 Received: 02/04/15 16:28 Matrix: Water Results Units Report Limit OF Prepared Analyzed CAS No. Qual Analytical Method: SM 6200B j NO ug/L 1.0 1 02/11/15 11:50 106-93-4 102 % 70-130 1 02/11/15 11:50 460-00-4 109 % Analytical Analytical Analytical Analytical 70-130 1 02/11/15 11:50 17060-07-0 100 % 70-130 1 02/11/16 11:50 2037-26-5 Method: SM 4500-S2D NO mg/L 0.10 1 02/05/1511:00 18496-25-8 Method: EPA 300.0 76.7 mg/L 4.0 2 02107/1610:39 14808-79-8 Method: EPA 353.2 0.29 mg/L 0.020 1 02/05/15 00:30 Method: SM 5310B 17.8 mg/L 1.0 1 02/05/15 20:56 7440-44-0 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. l i l Page 22 of 40 d� aceAnalytical www.pacelabs.com I g ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: WSW-4 Parameters Lab ID: 92236396010 Collected: 02/04/15 15:30 Results Units Report Limit DF Received: 02/04/15 16:28 Matrix: Water Prepared Analyzed CAS No. 601 Volatiles by SM 6200 Analytical Method: SM 6200B 1,1-Dichloroethane ND ug/L 1.0 1 02/11/15 12:07 75-34-3 1,1-Dichloroethene ND ug/L 1.0 1 02/11/15 12:07 75-35-4 - 1,1,1-Trichloroethane ND ug/L 1.0 1 02111/1512:07 71-55-6 1,1,2-Trichloroethane ND ug/L 1.0 1 02/11/15 12:07 79-00-5 1,1,2,2-Tetrachloroethane ND ug/L 1.0 1 02/11/15 12:07 79-34-5 1,2-Dichlorobenzene ND ug/L 1.0 1 02/11/15 12:07 95-50-1 1,2-Dichloroethane ND ug/L 1.0 1 02/11/15 12:07 107-06-2 1,2-Dichloropropane ND ug/L 1.0 1 02/11/15 12:07 78-87-5 1,3-Dichlorobenzene ND ug/L 1.0 1 02/11/15 12:07 541-73-1 1,4-Dichlorobenzene ND ug/L 1.0 1 02/11/15 12:07 10646-7 Bromodichloromethane ND ug/L 1.0 1 02111/1512:07 75-274 Bromomethane ND ug/L 5.0 1 02111/1512:07 74-83-9 Bromoform ND ug/L 1.0 1 02/11/15 12:07 75-25-2 cis-1,2-Dichloroethene ND ug/L 1.0 1 0211111512:07 156-59-2 cis-1,3-Dichloropropene ND ug/L 1.0 1 02111/1512:07 10061-01-5 Carbon tetrachloride ND ug/L 1.0 1 02/11/15 12:07 56-23-5 Chlorobenzene ND ug/L 1.0 1 02/11/15 12:07 108-90-7 Chloroethane ND ug/L 1.0 1 02/11/15 12:07 75-00-3 Chloroform ND ug/L 1.0 1 02/11/15 12:07 67-66-3 Chloromethane ND ug/L 1.0 1 02/11/15 12:07 74-87-3 Dibromochloromethane ND ug/L 1.0 1 02/11/15 12:07 12448-1 Dichlorodifluoromethane ND ug/L 1.0 1 02/11/15 12:07 75-71-8 Methylene Chloride ND ug/L 2.0 1 02/11/15 12:07 75-09-2 trans-1,2-Dichloroethene ND ug/L 1.0 1 02/11/15 12:07 156-60-5 trans-1,3-Dichloropropene ND ug/L 1.0 1 02/11/15 12:07 10061-02-6 Tetrachloroethene ND ug/L 1.0 1 02/11/15 12:07 127-18-4 Trichloroethene ND ug/L 1.0 1 02/11/15 12:07 79-01-6 Tdchlorofluoromethane ND ug/L 1.0 1 02/11/15 12:07 75-69-4 Vinyl chloride ND ug/L 1.0 1 02/11/15 12:07 75-014 1,2-Dibromoethane (EDB) ND ug/L 1.0 1 02/11/15 12:07 106-93-4 Surrogates 4-Bromofluorobenzene (S) 102 % 70-130 1 02/11/15 12:07 460-00-4 1,2-Dichloroethane-d4 (S) 110 % 70-130 1 02/11/15 12:07 17060-07-0 Toluene-d8 (S) 102 % 70-130 1 02/11/15 12:07 2037-26-5 Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. _ Qual Page 23 of 40 aceAnalytical www.pacelabs.com Pace Analytical Services, Inc. ' 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 ; i i QUALITY CONTROL DATA -, �I Project: DOT-504 34613.3.26 Pace Project No.: 92236396 QC Batch: AIR/22451 Analysis Method: RSK 175 i QC Batch Method: RSK 175 Analysis Description: RSK 175 AIR HEADSPACE Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, - 92236396008,92236396009 METHOD BLANK: 1895844 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Ethane ug/L ND 6.2 02106/1516:03 Ethene ug/L ND 6.2 02106/1516:03 Methane ug/L ND 6.6 02/06/1516:03 LABORATORY CONTROL SAMPLE & LCSD: 1895845 1895846 Spike LCS LCSD LCS LCSD % Rec Max Parameter Units Conc. Result Result % Rec % Rec Limits RPD RPD Qualifiers Ethane ug/L 114 108 109 95 96 85-115 2 20 Ethene ug/L 106 100 101 95 95 85-115 1 20 Methane ug/L 60.7 56.2 56.4 93 93 85-115 0 20 SAMPLE DUPLICATE: 1895847 10296012001 Dup Parameter Units Result Result RPD Qualifiers Ethane ug/L ND ND Ethene ug/L ND ND Methane ug/L 31.7 31.0 2 r SAMPLE DUPLICATE: 1895848 10296012004 Dup - Parameter Units Result Result RPD Qualifiers Ethane ug/L ND ND I Ethene ug/L ND ND Methane ug/L 9070 9830 8 E i Results presented on this page are I In the units Indicated by the "Units" column except where an alternate unit is presented to the right of the result REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, — Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 24 of 40 I I l aceAnalytical www..pacelabs.com i Project: DOT-504 34613.3.26 Pace Project No.: 92236396 QUALITY CONTROL DATA Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch: MERP/7557 Analysis Method: EPA 7470 QC Batch Method: EPA 7470 Analysis Description: 7470 Mercury Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 r METHOD BLANK: 1386127 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Mercury ug/L ND 0.20 02/0611516:19 _i LABORATORY CONTROL SAMPLE: 1386128 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Mercury ug/L 2.5 2.4 94 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1386129 1386130 MS MSD 92236289001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Mercury ug/L ND 2.5 2.5 2.4 2.4 98 98 75-125 0 — Results presented on this page are in the units Indicated by the "Units' column except where an alternate unit Is presented to the right of the result. r Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 25 of 40 acmnalytical w m..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 1 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 - Huntersville, NC 28078 (704)875-9092 t QC Batch: MPRP/17846 Analysis Method: EPA6010 j QC Batch Method: EPA 3010 Analysis Description: 6010 MET Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008 QUALITY CONTROL DATA METHOD BLANK: 1385562 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Arsenic ug/L ND 10.0 02/06/15 01:45 Barium ug/L ND 5.0 02/06/15 01:45 Cadmium ug/L ND 1.0 02/06/15 01:45 Chromium ug/L ND 5.0 02/06/15 01:45 Lead ug/L ND 5.0 02/06/15 01:45 Selenium ug/L ND 10.0 02/06/15 01:45 Silver ug/L ND 5.0 02/06/15 01:45 LABORATORY CONTROL SAMPLE: Parameter 1385563 Units Spike Cone. LCS Result LCS % Rec % Rec Limits Qualifiers Arsenic ug/L 500 457 91 80-120 Barium ug/L 500 463 93 80-120 Cadmium ug/L 500 467 93 80-120 Chromium ug/L 500 476 95 80-120 Lead ug/L 500 467 93 80-120 Selenium ug/L 500 462 92 80-120 Silver ug/L 250 237 95 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1385564 1385565 MS MSD 92235846002 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual Arsenic ug/L 103 500 500 488 482 77 76 75-125 1 Barium ug/L 113 500 500 870 849 151 147 75-125 3 M1 Cadmium ug/L 1 A 500 500 408 403 81 80 75-125 1 Chromium ug/L 255 500 500 666 659 82 81 75-125 1 Lead ug/L 17.6 500 500 443 435 85 84 75-125 2 Selenium ug/L 20.8 500 500 380 378 72 71 75-125 1 M1 Silver ug/L ND 250 250 204 201 81 80 75-125 1 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 26 of 40 lacieAnalyficalo www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 QUALITY CONTROL DATA Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch: MPRP/17852 Analysis Method: EPA6010 QC Batch Method: EPA3010 Analysis Description: 6010 MET Associated Lab Samples: 92236396009 METHOD BLANK: 1386032 Matrix: Water Associated Lab Samples: 92236396009 - Blank Reporting Parameter Units Result Limit Analyzed Qualifiers J Arsenic ug/L ND 10.0 02106/1518:26 Barium ug/L ND 5.0 02106/1518:26 Cadmium ug/L ND 1.0 02/06/1518:26 Chromium ug/L ND 5.0 02/06/1518:26 Lead ug/L ND 5.0 02/06/1518:26 Selenium ug/L ND 10.0 02106/1518:26 Silver ug/L ND 5.0 02106/1518:26 LABORATORY CONTROL SAMPLE: 1386033 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Arsenic ug/L 500 485 97 80-120 1 Barium ug/L 500 494 99 80-120 Cadmium ug/L 500 495 99 80-120 Chromium ug/L 500 474 95 80-120 Lead ug/L 500 481 96 80-120 Selenium ug/L 500 497 99 80-120 Silver ug/L 250 248 99 80-120 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1386034 1386035 MS MSD 92236396009 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result- Result % Rec % Rec Limits RPD Arsenic ug/L ND 500 500 512 509 102 102 75-125 1 — Barium ug/L 209 500 500 721 718 102 102 75-125 0 Cadmium ug/L ND 500 500 517 516 103 103 75-125 0 Chromium ug/L 79.0 500 500 555 555 95 95 75-125 0 i Lead ug/L ND 500 500 496 495 98 98 75-125 0 — Selenium ug/L ND 500 500 518 518 103 103 75-125 0 Silver ug/L ND 250 250 257 256 103 102 75-125 0 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, withoutthe written consent of Pace Analytical Services, Inc.. Qual Page 27 of 40 Analytical o www..pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. te loo 9800Huntersv Ile, NC'28078 (704)875-9092 -- QUALITY CONTROL DATA - -. QC Batch: MSV/30281 Analysis Method: SM 6200B QC Batch Method: SM 6200B Analysis Description: 601 by 6200B Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009,92236396010 METHOD BLANK: 1388284 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009,92236396010 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers 1,1,1-Trichloroethane ug/L ND 1.0 02/11/15 09:35 1,1,2,2-Tetrachloroethane ug/L ND 1.0 02/11/15 09:35 1,1,2-Trichloroethane ug/L ND 1.0 02/11/15 09:35 1,1-Dichloroethane ug/L ND 1.0 02/11/15 09:35 1,1-Dichloroethene ug/L ND 1.0 02/11/15 09:35 1,2-Dibromoethane (EDB) ug/L ND 1.0 02/11/15 09:35 1,2-Dichlorobenzene ug/L ND 1.0 02/11/15 09:35 1,2-Dichloroethane ug/L ND 1.0 02/11/15 09:35 _ 1,2-Dichloropropane ug/L ND 1.0 02/11/15 09:35 1,3-Dichlorobenzene ug/L ND 1.0 02/11/15 09:35 1,4-Dichlorobenzene ug/L ND 1.0 02/1111509:35 Bromodichloromethane ug/L ND 1.0 02/11/15 09:35 Bromoform ug/L ND 1.0 02/11/15 09:35 Bromomethane ug/L ND 5.0 02/11/15 09:35 Carbon tetrachloride ug/L ND 1.0 02M1/15 09:35 Chlorobenzene ug/L ND 1.0 02/11/15 09:35 Chloroethane ug/L ND 1.0 02/11/15 09:35 Chloroform ug/L ND 1.0 02/11/15 09:35 Chloromethane ug/L ND 1.0 02/11/15 09:35 cis-1,2-Dichloroethene ug/L ND 1.0 02/11/15 09:35 cis-1,3-Dichloropropene ug/L ND 1.0 02/11/15 09:35 - Dibromochloromethane ug/L ND 1.0 02/11/15 09:35 Dichlorodifluoromethane ug/L ND 1.0 02/11/15 09:35 Methylene Chloride ug/L ND 2.0 02/11/15 09:35 Tetrachloroethene ug/L ND 1.0 02/11/15 09:35 trans-1,2-Dichloroethene ug/L ND 1.0 02/11/15 09:35 trans-1,3-Dichloropropene ug/L ND 1.0 02/11/15 09:35 Trichloroethene ug/L ND 1.0 02/11/15 09:35 Trichlorofluoromethane ug/L ND 1.0 02/11/15 09:35 Vinyl chloride ug/L ND 1.0 02/11/15 09:35 1,2-Dichloroethane-d4 (S) % 104 70-130 02/11/15 09:35 4-Bromofluorobenzene (S) % 104 70-130 02/11/15 09:35 Toluene-d8 (S) % 100 70-130 02/11/15 09:35 as LABORATORY CONTROL SAMPLE: 1388285 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers 1,1,1-Trichloroethane ug/L 50 54.3 109 60-140 Results presented an this page are in the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS I This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 28 of 40 1�5acieAnalyticalo www.pacelabs.com i QUALITY CONTROL DATA - Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 LABORATORY CONTROL SAMPLE: 1388285 - Spike LCS LCS % Rec Parameter Units Cone. Result % Rec Limits Qualifiers 1,1,2,2-Tetrachloroethane ug/L 50 47.9 96 60-140 1,1,2-Trichloroethane ug/L 50 54.6 109 60-140 1,1-Dichloroethane ug/L 50 53.2 106 60-140 - 1,1-Dichloroethene ug/L 50 52.8 106 60-140 1,2-Dibromoethane (EDB) ug/L 50 49.7 99 60-140 1,2-Dichlorobenzene ug/L 50 45.1 90 60-140 1,2-Dichloroethane ug/L 50 57.3 115 60-140 1,2-Dichloropropane ug/L 50 50.2 100 60-140 1,3-Dichlorobenzene ug/L 50 44.0 88 60-140 1,4-Dichlorobenzene ug/L 50 44.0 88 60-140 Bromodichloromethane ug/L 50 51.9 104 60-140 Bromoform ug/L 50 43.3 87 60-140 Bromomethane ug/L 50 62.5 125 60-140 - Carbon tetrachloride ug/L 50 51.4 103 60-140 Chlorobenzene ug/L 50 46.1 92 60-140 Chloroethane ug/L 50 58.0 116 60-140 Chloroform ug/L 50 50.2 100 60-140 Chloromethane ug/L 50 52.2 104 60-140 cis-1,2-Dichloroethene ug/L 50 55.5 111 60-140 - cis-1,3-Dichloropropene ug/L 50 53.6 107 60-140 Dibromochloromethane ug/L 50 49.0 98 60-140 Dichlorodifluoromethane ug/L 50 54.4 109 60-140 Methylene Chloride ug/L 50 58.7 117 60-140 Tetrachloroethene ug/L 50 44.8 90 60-140 trans-1,2-Dichloroethene ug/L 50 53.4 107 60-140 trans-1,3-Dichloropropene ug/L 50 56.6 113 60-140 Trchloroethene ug/L 50 49.8 100 60-140 Trichlorofluoromethane ug/L - 50 58.2 116 60-140 Vinyl chloride ug/L 50 51.3 103 60-140 1,2-Dichloroethane-d4 (S) % 104 70-130 4-Bromofluorobenzene (S) % 109 70-130 Toluene-d8 (S) % 103 70-130 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1388286 1388287 MS MSD 92236396010 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD 1,1,1-Trichloroethane ug/L ND 20 20 21.1 15.9 105 80 60-140 28 1,1,2,2-Tetrachloroelhane ug/L ND 20 20 17.2 14.1 86 71 60-140 19 1,1,2-Trichloroethane ug/L ND 20 20 19.9 15.4 100 77 60-140 25 1,1-Dichloroethane ug/L ND 20 20 21.0 16.0 105 80 60-140 27 -' 1,1-Dichloroethene ug/L ND 20 20 21.7 16.2 108 81 60-140 29 1,2-Dibromoethane (EDB) ug/L ND 20 20 17.2 14.0 86 70 60-140 20 1,2-Dichlorobenzene ug/L ND 20 20 16.5 12.7 82 64 60-140 26 1,2-Dichloroethane ug/L ND 20 20 21.5 16.3 108 81 60-140 28 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Qua[ Page 29 of 40 1�55'cmnalydca( www.pacelabs.com I QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 i MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1388286 1388287 MS MSD 92236396010 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qua[ 1,2-Dichloropropane ug/L ND 20 20 19.0 14.3 95 72 60-140 28 1,3-Dichlorobenzene ug/L ND 20 20 16.3 12.4 82 62 60-140 27 1,4-Dichlorobenzene ug/L ND 20 20 16.6 12.7 83 64 60-140 26 Bromodichloromethane ug/L ND 20 20 18.4 13.8 92 69 60-140 29 Bromoform ug/L ND 20 20 14.9 12.3 74 62 60-140 19 Bromomethane ug/L ND 20 20 26.9 18.1 135 91 60-140 39 R1 Carbon tetrachloride ug/L ND 20 20 19.8 15.2 99 76 60-140 26 Chlorobenzene ug/L ND 20 20 17.3 13.7 87 68 60-140 24 Chloroethane ug/L ND 20 20 27.5 19.1 138 96 60-140 36 R1 Chloroform ug/L ND 20 20 19.4 14.8 97 74 60-140 27 Chloromethane ug/L ND 20 20 21.2 15.7 106 78 60-140 30 cis-1,2-Dichloroethene ug/L ND 20 20 21.7 16.3 108 82 60-140 28 cis-1,3-Dichloropropene ug/L ND 20 20 18.3 14.2 91 71 60-140 25 Dibromochloromethane ug/L ND 20 20 15.3 11.8 77 59 60-140 26 MO Dichlorodifluoromethane ug/L ND 20 20 23.3 17.6 117 88 60-140 28 Methylene Chloride ug/L ND 20 20 21.0 15.2 105 76 60-140 32 R1 Tetrachloroethene ug/L ND 20 20 17.1 14.1 85 71 60-140 19 trans-1,2-Dichloroethene ug/L ND 20 20 21.2 16.2 106 81 60-140 27 trans-1,3-Dichloropropene ug/L ND 20 20 18.7 14.2 94 71 60-140 28 Trichloroethene ug/L ND 20 20 19.2 15.0 96 75 60-140 25 Trichlorofluoromethane ug/L ND 20 20 25.6 19.1 128 96 60-140 29 Vinyl chloride ug/L ND 20 20 21.3 15.7 106 78 60-140 30 1,2-Dichloroethane-d4 (S) % 109 105 70-130 4-Bromofluorobenzene (S) % 106 109 70-130 Toluene-d8 (S) % 103 103 70-130 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 30 of 40 1 - 5aneAnalytical" www.pacelabs.com I ! Project: DOT-504 34613.3.26 Pace Project No.: 92236396 QUALITY CONTROL DATA QC Batch: WET/35567 Analysis Method: SM 4500-S2D - QC Batch Method: SM 4500-S2D Analysis Description: 4500S213 Sulfide Water Associated Lab Samples: 92236396002, 92236396005, 92236396007, 92236396009 METHOD BLANK: 1385059 Matrix: Water Associated Lab Samples: 92236396002, 92236396005, 92236396007, 92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfide mg/L ND 0.10 0210511511:00 LABORATORY CONTROL SAMPLE: 1385060 Parameter Units Sulfide mg/L Spike LCS Cone. Result .5 0.49 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 LCS % Rec % Rec Limits Qualifiers 99 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1385061 1385062 MS MSD 92235628002 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual I � Sulfide mg/L ND .5 .5 0.48 0.48 90 90 90-110 0 Results presented on this page are to the units indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 31 of 40 acmnalytical www.pacelabs.com QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92236396 QC Batch: WET/35601 Analysis Method: SM 4500-S2D QC Batch Method: SM 4500-S2D Analysis Description: 4500S2D Sulfide Water Associated Lab Samples: 92236396001, 92236396003, 92236396004, 92236396006, 92236396008 METHOD BLANK: 1386390 Matrix: Water Associated Lab Samples: 92236396001, 92236396003, 92236396004, 92236396006, 92236396008 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfide mg/L ND 0.10 02/06/1516:45 Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 Huntersville, NC 28078 (704)875-9092 l LABORATORY CONTROL SAMPLE: 1386391 Spike LCS LCS % Rec Parameter. Units Conc. Result % Rec Limits Qualifiers Sulfide mg/L .5 0.50 101 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1386392 1386393 MS MSD 92236233001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Conc. Conc. Result Result % Rec % Rec Limits RPD Qual Sulfide mg/L NO .5 .5 0.48 0.49 97 97 90-110 0 Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right or the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. I Page 32 of 40 J, Pace Analytical Services, Inc. g n ® 9800 Kincey Ave. Suite 100 �ceAnal �/tical Huntersville, NC 28078 www.pacelabs.com (704)875-9092 - -, QUALITY CONTROL DATA Project: DOT 504 34613.3.26 Pace Project No.: 92236396 QC Batch: WETA/21832 Analysis Method: EPA 300.0 QC Batch Method: EPA 300.0 Analysis Description: 300.0 IC Anions Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 METHOD BLANK: 1386068 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Sulfate mg/L ND 2.0 02/06/1513:48 LABORATORY CONTROL SAMPLE: 1386069 Parameter Units Sulfate mg/L Spike Cone. 20 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1386070 MS 92236396001 Spike. Parameter Units Result Cone. Sulfate mg/L 19.0 20 LCS LCS - % Rec Result % Rec Limits Qualifiers 20.6 103 90-110 1386071 MSD Spike MS MSD MS MSD % Rec Cone. Result Result % Rec % Rec Limits RPD 20 39.0 40.2 100 106 90-110 3 Qual MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1386072 1386073 MS MSD 92236646002 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qual Sulfate mg/L 7810 20 20 7810 7780 -2 -155 90-110 0 M6 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 33 of 40 lacieAnalyticalo www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 - i QC Batch: WETA/21813 Analysis Method: EPA 353.2 QC Batch Method: EPA 353.2 Analysis Description: 353.2 Nitrate + Nitrite, Unpres. Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 METHOD BLANK: 1384756 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, —, 92236396008,92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Nitrogen, Nitrate mg/L ND 0.020 02/04/15 23:54 LABORATORY CONTROL SAMPLE: 1384757 Parameter Units Nitrogen, Nitrate mg/L QUALITY CONTROL DATA Spike LCS Cone. Result 2.5 2.5 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1384758 MS 92236183003 Spike Parameter Units Result Cone. Nitrogen, Nitrate mg/L 1.1 2.5 Qualifiers 1384759 -- MSD Spike MS MSD MS MSD % Rec Cone. Result Result % Rec % Rec Limits RPD Qua[ 2.5 3.1 3.4 79 93 90-110 11 M1,R1 LCS % Rec % Rec Limits 99 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1384760 1384761 MS MSD 92236230001 Spike Spike MS MSD MS MSD % Rec Parameter Units Result Cone. Cone. Result Result % Rec % Rec Limits RPD Qua[ Nitrogen, Nitrate mg/L 10.1 2.5 2.5 13.7 13.9 141 149 90-110 1 M1 Results presented on this page are in the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 34 of 40 j-i aceAnalytical www.pacelabs.com QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch: WETA/21815 Analysis Method: SM 5310B QC Batch Method: SM 5310B Analysis Description: 531013 TOC Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 METHOD BLANK: 1385102 Matrix: Water Associated Lab Samples: 92236396001, 92236396002, 92236396003, 92236396004, 92236396005, 92236396006, 92236396007, 92236396008,92236396009 Blank Reporting Parameter Units Result Limit Analyzed Qualifiers Total Organic Carbon mg/L ND 1.0 02/05/15 16:06 LABORATORY CONTROL SAMPLE: 1385103 Parameter Units Total Organic Carbon mg/L Spike LCS LCS % Rec _ Conc. Result % Rec Limits Qualifiers 25 24.2 97 90-110 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1385104 MS 92236210001 Spike Parameter Units Result Conc. Total Organic Carbon mg/L 724 25 MATRIX SPIKE & MATRIX SPIKE DUPLICATE: 1385106 MS 92236396004 Spike Parameter Units Result Conc. Total Organic Carbon mg/L 3.2 25 1385105 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD Qual 25 700 688 -98 -147 90-110 2 M6 1385107 MSD Spike MS MSD MS MSD % Rec Conc. Result Result % Rec % Rec Limits RPD Qua[ 25 28.2 28.0 100 99 90-110 1 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 35 of 40 aceAnalytical l VAMPacelabs.com QUALIFIERS Project: DOT-504 34613.3.26 Pace Project No.: 92236396 DEFINITIONS Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 DF - Dilution Factor, if reported, represents the factor applied to the reported data due to changes in sample preparation, dilution of the sample aliquot, or moisture content. ND - Not Detected at or above adjusted reporting limit. J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL -Adjusted Method Detection Limit. PQL - Practical Quantitation Limit. RL - Reporting Limit. S - Surrogate 1,2-Diphenylhydrazine (8270 listed analyte) decomposes toAzobenzene. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) -.Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean -Up U - Indicates the compound was analyzed for, but not detected. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA Method 8260. Acid preservation may not be appropriate for 2-Chloroethylvinyl ether, Styrene, and Vinyl chloride. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TN - The NELAC Institute. LABORATORIES PASI-A Pace Analytical Services -Asheville PAST-C Pace Analytical Services - Charlotte PASI-M Pace Analytical Services - Minneapolis ANALYTE QUALIFIERS E Analyte concentration exceeded the calibration range. The reported result is estimated. Mo Matrix spike recovery and/or matrix spike duplicate recovery was outside laboratory control limits. M1 Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery. M6 Matrix spike and Matrix spike duplicate recovery not evaluated against control limits due to sample dilution. R1 RPD value was outside control limits. Date: 02/11/2015 05:03 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 36 of 40 Z�;acmnalyfical www..pacelabs.com QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Lab ID Sample ID QC Batch Method QC Batch Analytical Method Analytical Batch 92236396001 DMW-10 RSK 175 AIR/22451 92236396002 DMW-6 RSK 175 AIR/22451 92236396003 DMW-7 RSK 175 AIR/22451 92236396004 DMW-9 RSK 175 AIR/22451 92236396005 DMW-8 RSK 175 AIR/22451 92236396006 DMW-11 RSK 175 AIR/22451 92236396007 DMW-2 RSK 175 AIR/22451 92236396008 DMW-1 RSK 175 AIR/22451 92236396009 DMW-3 RSK 175 AIR/22451 92236396001 DMW-10 EPA 3010 MPRP/17846 EPA 6010 ICP/16062 92236396002 DMW-6 EPA 3010 MPRP/17846 EPA 6010 ICP/16062 92236396003 DMW-7 EPA 3010 MPRP/17846 EPA6010 ICP/16062 92236396004 DMW-9 EPA 3010 MPRP/17846 EPA6010 ICP/16062 92236396005 DMW-8 EPA3010 MPRP/17846 EPA6010 ICP/16062 92236396006 DMW-11 EPA 3010 MPRP/17846 EPA6010 ICP/16062 92236396007 DMW-2 EPA 3010 MPRP/17846 EPA 6010 ICP/16062 92236396008 DMW-1 EPA 3010 MPRP/17846 EPA6010 ICP/16062 92236396009 DMW-3 EPA 3010 MPRP/17852 EPA 6010 ICP/16069 92236396001 DMW-10 EPA 7470 MERP/7557 EPA 7470 MERC/7251 92236396002 DMW-6 EPA 7470 MERP/7557 EPA 7470 MERC/7251 92236396003 DMW-7 EPA 7470 MERP/7557 EPA 7470 MERC/7251 92236396004 DMW-9 EPA 7470 MERP/7557 EPA 7470 MERC/7251 92236396005 DMW-8 EPA 7470 MERP/7557 EPA 7470 MERC17251 92236396006 DMW-11 EPA 7470 MERP/7557 EPA 7470 MERC17251 92236396007 DMW-2 EPA 7470 MERP/7557 EPA 7470 MERC17251 92236396008 DMW-1 EPA 7470 MERP/7557 EPA 7470 MERC17251 92236396009 DMW-3 EPA 7470 MERP/7557 EPA 7470 MERC/7251 92236396001 DMW-10 SM 6200B MSV/30281 92236396002 DMW-6 SM 6200E MSV/30281 92236396003 DMW-7 SM 6200B MSV/30281 92236396004 DMW-9 SM 6200B MSV/30281 92236396005 DMW-8 SM 6200E MSV/30281 92236396006 DMW-11 SM 6200E MSV/30281 92236396007 DMW-2 SM 6200B MSV/30281 92236396008 DMW-1 SM 6200B MSV/30281 92236396009 DMW-3 SM 6200E MSV/30281 92236396010 WSW-4 SM 6200B MSV/30281 92236396001 DMW-10 SM 4500-S2D WET/35601 92236396002 DMW-6 SM 4500-S2D WET/35567 92236396003 DMW-7 SM 4500-S2D WET/35601 92236396004 DMW-9 SM 4500-S213 WET/35601 92236396005 DMW-8 SM 4500-S2D WET/35567 92236396006 DMW-11 SM 4500-S213 WET/35601 92236396007 DMW-2 SM 4500-S213 WET/35567 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Page 37 of 40 aceAnalXical www.pacelabs.com I QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: DOT-504 34613.3.26 Pace Project No.: 92236396 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Lab ID Sample ID QC Batch Method QC Batch Analytical Method 92236396008 DMW-1 SM 4500-S2D WET/35601 92236396009 DMW-3 SM 4500-S2D WET/35567 92236396001 DMW-10 EPA 300.0 WETA/21832 92236396002 DMW-6 EPA 300.0 WETA/21832 92236396003 DMW-7 EPA 300.0 WETA121832 92236396004 DMW-9 EPA 300.0 WETA121832 92236396006 DMW-8 EPA 300.0 WETA/21832 92236396006 DMW-11 EPA 300.0 WETA/21832 92236396007 DMW-2 EPA 300.0 WETA/21832 92236396008 DMW-1 EPA 300.0 WETA121832 92236396009 DMW-3 EPA 300.0 WETA(21832 92236396001 DMW-10 EPA 353.2 WETA121813 92236396002 DMW-6 EPA 353.2 WETA/21813 92236396003 DMW-7 EPA 353.2 WETA121813 92236396004 DMW-9 EPA 353.2 WETA121813 92236396005 DMW-8 EPA 353.2 WETA121813 92236396006 DMW-11 EPA 353.2 WETA121813 92236396007 DMW-2 EPA 353.2 WETA/21813 92236396008 DMW-1 EPA 353.2 WETA121813 92236396009 DMW-3 EPA 353.2 WETA121813 92236396001 DMW-10 SM 5310B WETA121815 92236396002 DMW-6 SM 5310E WETA121815 92236396003 DMW-7 SM 5310E WETA/21815 92236396004 DMW-9 SM 5310B WETA121815 92236396005 DMW-8 SM 5310B WETA121815 92236396006 DMW-11 SM 5310B WETA121815 92236396007 DMW-2 SM 5310B WETA121815 92236396008 DMW-1 SM 5310B WETA121815 92236396009 DMW-3 SM 5310B WETA121815 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 02/11/2015 05:03 PM without the written consent of Pace Analytical Services, Inc.. Analytical Batch Page 38 of 40 or 1 05 acQAnaiyticai4 Sample Condition U on Recei t SCUR Page 1 of 2 Document Number: Issuing Authority: - F-CHR-CS-003-rev.15 Pace Huntersvilie Quality Office Client Name:_ Flu( �' -3 1-fidlMu,� Courier: ❑ Fed Ex ElUPS❑ USPS❑ ` Co Client mercial❑ Pace Other b -fit , Custody Seal on Cooler/Box Present: Elyes no Seals Intact: ❑ yes ❑ no Packing Material: ❑ Bubble VDp i Bubble Bags ❑ None ❑ Other Thermometer Used: IR Gun 61�ofType of Ice: V lue None amples on Ice, cooling process has begun Temp Correction Factor T1401 No Correction Corrected Cooler Temp.: •C Temp should be above freezing to VC Biological Tissue is Frozen: Yes No A Comments: t Date and In! Is -of person examiningcontents: Chain of Custody Present: No ❑NIA 1. Chain of Custody Filled Out: No ❑N►A 2. Chain of Custody Relinquished: 00y's--6w ❑NIA 3. Sampler Name & Signature on COC: s o ❑NIA 4, Samples Arrived within Hold Time: es ON9, ❑NIA 5. Short Hold Time Analysis (<72hr): es ❑No PNIA 6. Rush Turn Around Time Requested: ❑Yes NIA 7. Sufficient Volume: s ❑No N/A $. Correct Containers Used: -Pace Containers Used: es ❑N NIA es ❑N ❑NIA 9. Containers Intact: Bell --[]No ❑NIA 10. Filtered volume received for Dissolved tests ❑Yes ❑No fK 11. Sample Labels match COC: -Includes date/time/ID/Analysis Matrix: es ❑No ❑NIA 12. All containers needing preservation have been checked. All containers needing preservation are found to be In compliance with EPA recommendation. exceptions: VOA, coliform, TOC, O&G, VVI-DRO pvater) es ❑No !A ❑Yes ❑No NIA ❑ s ❑ 13. Samples checked for dechlorination: es ❑No ❑NIA 4. Headspace in VOA Vials ( >6mm): ❑Yes o ❑NIA 1 Trip Blank Present: Trip Blank Custody Seals Present Pace Trip Blank Lot # (if purchased): ❑Yes ❑No ❑Yes ❑No IA IA 1 Client Notification/ Resolution: Person Contacted: Daterrime: Comments/ Resolution: SCURF Review: jDate: 1 2 '( !S SRF Review: Date: 2 S Note: Whenever they . a discrepancy affecting North Carolina compliance samples, a copy of this form will be sent to the North Carolina DEHNR Certification Office ( Le out of hold, incorrect preservative, out of temp, Incorrect containers) Field Data Required? Y / N ----- 9226396 -- - IAo# `` ti11111�11�1 �1� ._... g2231396 „o label available) Page 39 of 40 r _ i CHAIN -OF -CUSTODY / Analytical Request Document w ,aceAna1Xica1' The Chain -of -Custody is a LEGAL DOCUMENT, All relevant fields must be completed accurately. ° • www.paeetabs.eem o N Section A Section B Section C Page. of IL Required Client Information: Required Project Information: Invoice Information: ///�-��� Company q N� Ct iGu`Kcto O Relxltt To: r 4�• bie�n J n Attention: � 9 0 1 s� 5 d �J �f Address: _a 2 d3 S o: �`- She' [O Copy To: Company Name: � REGULATORY AGENCY CGt�T.�d i✓C a J d 0f Address: f NPDES .f GROUND WATER r DRINKING WATER Email To: SLt%�� Glc-rr�'LfrctCsk�wC - Purchase Order No.: Paco quote Roforonea: — r ' RCRA OTHER USTte Phone: S w — c fax: Project Name: Paco Project Manager. Site Location STATE Av Z RequestedDue DatefiAT: ProjectNumber. PacoProneu �naCp DD Requested Analysis Filtered (YIN) Section D Matrix Codes Required Client Information MATRIX I CODE Drinking Water DW o — ; U COLLECTED z Water WT 1 (111 ° Waste Water WW M m COMPOSITE COMPOSITE Product p a START ENDIGRAS j SoiUSolid SL —� SAMPLE ID Wipe WP W (A-Z. 0-91;) Air AR z Sample IDS MUST BE UNIQUE Tissue TS O c- F Other OT U �: w Z it %: W U g a a ILL DATE TIME DATE TIME rn Preservatives O DO CO W J 7 ZO0 = Z Z O Q �► V , O V N Pace Project NoJ Lab 1. jam a I lnnf■�W= ■■stun rigi■■ii e n��■i■�■�n■unu■■t� ADDITIONAL COMMENTS RELNQUISHED, BY I AFFILIATION DATE TIME ACCEPTED BY I AFFILIATION DATE TIME SAMPLE CONDITIONS �(///S I(9-W 16 Z& ' 3 f.t(�-'(��r•� SAMPLERNAMEANDSIGNATURE PRINT Name of SAMPLER: S`Q �G S,M U a o� ao go z A c m z SIGNATURE of SAMPLER: DA7ESigned ]� [r% m N m U m a y E •Important Note., By signing this form you are accepting pace's NET 30 day payment terns and agmoing to late charges of 1.5% per month forany invoices (MMIDD/YY): 30 m days. F-ALL-0-020rev.07, 15-May-2007 aceAnalXical www.pacelabs.com June 10, 2015 Chemical Testing Engineer NCDOT Materials & Tests Unit 1801 Blue Ridge Road Raleigh, NC 27607 RE: Project: DOT-504 34613.3.26 Pace Project No.: 92252375 Dear Chemical Engineer: Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Enclosed are the analytical results for sample(s) received by the laboratory on June 02, 2015. The results relate only to the samples included in this report. Results reported herein conform to the most current TNI standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report. Analyses were performed at the Pace Analytical Services location indicated on the sample analyte page for analysis unless otherwise footnoted. If you have any questions concerning this report, please feel free to contact me. Sincerely, Kevin Godwin kevin.godwin@pacelabs.com Project Manager Enclosures REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 1 of 11 aceAnaVical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92252375 Charlotte Certification IDs 9800 Kincey Ave. Ste 100, Huntersville, NC 28078 North Carolina Drinking Water Certification #: 37706 North Carolina Field Services Certification #: 5342 North Carolina Wastewater Certification #: 12 South Carolina Certification M 99006001 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 i CERTIFICATIONS - I Florida/NELAP Certification #: E87627 Kentucky UST Certification M 84 West Virginia Certification M 357 vrginiaNELAP Certification M 460221 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 2 of 11 - aceAnalytical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92252375 Lab ID Sample ID 92252375001 SS-2 i SAMPLE SUMMARY Matrix Date Collected Date Received Water 06/02/1514:00 06/02/1514:44 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Page 3 of 11 acmnalytical www.pacelabs.com SAMPLE ANALYTE COUNT Project: DOT-504 34613.3.26 Pace Project No.: 92252375 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Analytes Lab ID Sample ID Method Analysts Reported Laboratory 92252375001 SS-2 SM 6200B CAH 33 PASI-C REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 4 of 11 aceAnalytical www.pecolabs.com '1 ANALYTICAL RESULTS Project: DOT-504 34613.3.26 Pace Project No.: 92252375 Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 Huntersville, NC 28078 (704)875-9092 Sample: SS-2 Lab ID: 92252375001 Collected: 06/02/15 14:00 Received: 06/02/15 14:44 Matrix: Water Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual 601 Volatiles by SM 6200 1,1-Dichloroethane 1,1-Dichloroethene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2,2-Tetrachloroethane 1,2-Dichlorobenzene -, 1,2-Dichloroethane 1,2-Dichloropropane 1,3-Dichlorobenzene 1,4-Dichlorobenzene Bromodichloromethane Bromomethane Bromoform cis-1,2-Dichloroethene cis-1,3-Dichloropropene Carbon tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Dibromochloromethane Dichlorodifluoromethane Methylene Chloride trans-1,2-Dichloroethene trans-1,3-Dichloropropene Tetrachloroethene Trchloroethene Trichlorofluoromethane Vinyl chloride 1,2-Dibromoethane (EDB) Surrogates 4-Bromofluorobenzene (S) 1,2-Dichloroethane-d4 (S) Toluene-d8 (S) Date: 06/10/2015 02:38 PM Analytical Method: SM 6200B ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L ND ug/L 102 % 92 % 100 % 1.0 1 06/10/15 06:36 75-34-3 1.0 1 06/10/15 06:36 75-35-4 1.0 1 06/10/15 06:36 71-55-6 1.0 1 06/10/15 06:36 79-00-5 1.0 1 06/10/15 06:36 79-34-5 1.0 1 06/10/15 06:36 95-50-1 1.0 1 06/10/15 06:36 107-06-2 1.0 1 06/10/15 06:36 78-87-5 1.0 1 06/10/15 06:36 541-73-1 1.0 1 06/10/15 06:36 106-46-7 1.0 1 06/10/15 06:36 75-27-4 5.0 1 06/10/15 06:36 74-83-9 1.0 1 06/10/15 06:36 75-25-2 1.0 1 06/10/15 06:36 156-59-2 1.0 1 06/10/15 06:36 10061-01-5 1.0 1 06/10/15 06:36 56-23-5 1.0 1 06/10/15 06:36 108-90-7 1.0 1 06/10/15 06:36 75-00-3 1.0 1 06/10/15 06:36 67-66-3 1.0 1 06/10/15 06:36 74-87-3 1.0 1 06/10/15 06:36 124-48-1 1.0 1 06/10/15 06:36 75-71-8 2.0 1 06/10/15 06:36 75-09-2 1.0 1 06/10/15 06:36 156-60-5 1.0 1 06/10/15 06:36 10061-02-6 1.0 1 06/10/15 06:36 127-18-4 1.0 1 06/10/15 06:36 79-01-6 1.0 1 06/10/15 06:36 75-69-4 1.0 1 06/10/15 06:36 75-01-4 1.0 1 06/10/15 06:36 106-93-4 70-130 1 06/10/15 06:36 460-00-4 70-130 1 06/10/15 06:36 17060-07-0 70-130 1 06/10/15 06:36 2037-26-5 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 5 of 11 acmnalXical www.pacelabs.com Project: DOT-504 34613.3.26 Pace Project No.: 92262375 QC Batch: MSV/32056 QC Batch Method: SM 6200B Associated Lab Samples: 92252375001 QUALITY CONTROL DATA Analysis Method: SM 6200B Analysis Description: 601 by 6200E METHOD BLANK: 1479953 Associated Lab Samples: 92252375001 Parameter Units Matrix: Water Blank Reporting Result Limit Analyzed 1,1,1-Trichloroethane ug/L ND 1.0 06/10/15 00:31 1,1,2,2-Tetrachloroethane ug/L ND 1.0 06/10/15 00:31 1,1,2-Trichloroethane ug/L ND 1.0 06/10/15 00:31 1,1-Dichloroethane ug/L ND 1.0 06/10/15 00:31 1,1-Dichloroethene ug/L ND 1.0 06/10/15 00:31 1,2-Dibromoethane (EDB) ug/L ND 1.0 06/10/15 00:31 1,2-Dichlorobenzene ug/L ND 1.0 06/10/15 00:31 1,2-Dichloroethane ug/L ND 1.0 06/10/15 00:31 1,2-Dichloropropane ug/L ND 1.0 06/10/15 00:31 1,3-Dichlorobenzene ug/L ND 1.0 06/10/15 00:31 1,4-Dichlorobenzene ug/L ND 1.0 06/10/15 00:31 Bromodichloromethane ug/L ND 1.0 06/10/15 00:31 Bromoform ug/L ND 1.0 06/10/15 00:31 Bromomethane ug/L ND 5.0 06/10/15 00:31 Carbon tetrachloride ug/L ND 1.0 06/10/15 00:31 Chlorobenzene ug/L ND 1.0 06/10/15 00:31 Chloroethane ug/L ND 1.0 06/10/15 00:31 Chloroform ug/L ND 1.0 06/10/15 00:31 Chloromethane ug/L ND 1.0 06/10/15 00:31 cis-1,2-Dichloroethene ug/L ND 1.0 06/10/15 00:31 cis-1,3-Dichloropropene ug/L ND 1.0 06/10/15 00:31 Dibromochloromethane ug/L ND 1.0 06/10/15 00:31 Dichlorodifluoromethane ug/L ND 1.0 06/10/15 00:31 Methylene Chloride ug/L ND 2.0 06/10/15 00:31 Tetrachloroethene ug/L ND 1.0 06/10/15 00:31 trans-1,2-Dichloroethene ug/L ND 1.0 06/10/15 00:31 trans-1,3-Dichloropropene ug/L ND 1.0 06/10/15 00:31 Trichloroethene ug/L ND 1.0 06/10/15 00:31 Trichlorofluoromethane ug/L ND 1.0 06/10/15 00:31 Vinyl chloride ug/L ND 1.0 06/10/15 00:31 1,2-Dichloroethane-d4 (S) % 90 70-130 06/10/15 00:31 4-Bromofluorobenzene (S) % 101 70-130 06/10/15 00:31 Toluene-d8 (S) % 98 70-130 06/10/15 00:31 LABORATORY CONTROL SAMPLE: 1479954 Qualifiers Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers 1,1,1-Trichloroethane ug/L 50 46.0 92 60-140 1,1,2,2-Tetrachloroethane ug/L 50 48.3 97 60-140 1,1,2-Trichloroethane ug/L 50 48.5 97 60-140 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 06/10/2015 02:38 PM without the written consent of Pace Analytical Services, Inc.. Page 6 of 11 aceAnalytical www..pacelabs.com QUALITY CONTROL DATA Project: DOT-504 34613.3.26 Pace Project No.: 92252375 LABORATORY CONTROL SAMPLE: 1479954 Parameter Units Spike Conc. LCS Result LCS % Rec % Rec Limits 1,1-Dichloroethane ug/L 50 47.0 94 60-140 1,1-Dichloroethene ug/L 50 44.0 88 60-140 1,2-Dibromoethane (EDB) ug/L 50 50.2 100 60-140 1,2-Dichlorobenzene ug/L 50 51.1 102 60-140 1,2-Dichloroethane ug/L 50 47.0 94 60-140 1,2-Dichloropropane ug/L 50 49.0 98 60-140 1,3-Dichlorobenzene ug/L 50 49.2 98 60-140 1,4-Dichlorobenzene ug/L 50 50.0 100 60-140 Bromodichloromethane ug/L 50 45.0 90 60-140 Bromoform ug/L 50 45.6 91 60-140 Bromomethane ug/L 50 42.1 84 60-140 Carbon tetrachloride ug/L 50 48.9 98 60-140 Chlorobenzene ug/L 50 51.3 103 60-140 Chloroethane ug/L 50 43.5 87 60-140 Chloroform ug/L 50 43.4 87 60-140 Chloromethane ug/L 50 36.7 73 60-140 cis-1,2-Dichloroethene ug/L 50 47.6 95 60-140 cis-1,3-Dichloropropene ug/L 50 47.6 95 60-140 Dibromochloromethane ug/L 50 45.2 90 60-140 Dichlorodifluoromethane ug/L 50 37.8 76 60-140 Methylene Chloride ug/L 50 47.6 95 60-140 Tetrachloroethene ug/L 50 49.1 98 60-140 trans-1,2-Dichloroethene ug/L 50 46.1 92 60-140 trans-1,3-Dichloropropene ug/L 50 48.2 96 60-140 Trichloroethene ug/L 50 49.3 99 60-140 Trichlorofluoromethane ug/L 50 41.3 83 60-140 Vinyl chloride ug/L 50 41.2 82 60-140 1,2-Dichloroethane-d4 (S) % 91 70-130 4-Bromofluorobenzene (S) % 102 70-130 Toluene -dB (S) % 98 70-130 Pace Analytical Services, Inc. 9800 Kincey Ave. Suite 100 Huntersville, NC 28078 (704)875-9092 Qualifiers Results presented on this page are In the units Indicated by the "Units" column except where an alternate unit Is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full. Date: 06110/2015 02:38 PM without the written consent of Pace Analytical Services, Inc.. Page 7 of 11 acmnalytical www..pacelabs.com QUALIFIERS Project: DOT-504 34613.3.26 Pace Project No.: 92252375 DEFINITIONS Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 Huntersville, NC 28078 (704)875-9092 DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot. ND - Not Detected at or above adjusted reporting limit. J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL -Adjusted Method Detection Limit. PQL- Practical Quantitation Limit. RL- Reporting Limit. S - Surrogate 1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is a combined concentration. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean -Up U - Indicates the compound was analyzed for, but not detected. Acid preservation may not be appropriate for 2 Chloroethylvinyl ether, Styrene, and Vinyl chloride. A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA Method 8260. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TNI - The NELAC Institute. LABORATORIES PASI-C Pace Analytical Services - Charlotte Date: 06/10/2015 02:38 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Page 8 of 11 r � JI (I�IacieAnalytkal www.pacelabs.com QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: DOT 504 34613.3.26 Pace Project No.: 92252375 - Lab ID Sample ID 92252375001 SS-2 Date: 06/10/2015 02:38 PM Pace Analytical Services, Inc. 9800 KinceyAve. Suite 100 Huntersville, NC 28078 (704)875-9092 QC Batch Method QC Batch Analytical Method SM 6200B MSV/32056 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, Inc.. Analytical Batch Page 9 of 11 (--11'11100h1111X1081* Condltion Upon Receil Document Number: F-CHR-CS-003-rev.16 Client iVame:_ 14 H / -� i tt � � 11 /"i U � * Page,2 of 2 is for Internal Use Only Courier: ❑ Fed Ex ❑ UPS❑ LISPS❑ Client C merclal❑ ��—Other my'. Custody Seal on Cooler/Box Present- ❑ yes no Seals intact:yes ❑ no Packing Material: ❑ Bubbie �p ubble Bags ❑ None ❑ Other Page 1 of 2* Office Thermometer Used: IR Gun 140 Type of Ice: Blue None Sm les on ice, cooling process has begun Temp Correction Factor T1401 No Correction Corrected Cooler Temp.: I. •C Temp should be above freezing to 6°C Biological Tissue is Frozen: Yes NotC!: Comments: Initials7�7!rson exaaqq��I Inn ts: C d Chan'of Custody Present: es 0 ❑N/A 1. 2. 3, Chain of Custody Filled Out: es o ❑N►A Chain of Custody Relinquished: Yes (❑N/A Sampler Name & Signature on COC: es ❑ ❑N/A 4. Samples Arrived within Hold Time: es ❑No A 5. Short Hold Time Analysis <72hr): []yes 13 0 ❑ A 6. Rush Turn Around Time Requested: Dyes ❑N/A 7. Sufficient Volume: es o ❑NIA 8. Correct Containers Used: -Pace Containers Used: Yes o Yes o ❑N/A ❑N/A 9. Containers Intact: flYes ❑No ❑N/A 1 11. Filtered volume received for Dissolved tests ❑Yes ❑ o•• rA Sample Labels match COC: -Includes date/time/ID/Analysis Matrix: es' ❑No Y ❑N/A 12. All containers needing preservation have been checked. All containers needing preservation are found to be in compliance with EPA recommendation. exceptlons: VOA, MUM. TOG, 0&G. WI-DRO (water) ❑Yes []No ❑ !A []Yes N/A 11Yes []No 1 Samples checked for dechlorination: ❑Yes ❑No r 4, t eadspace in VOA Vials (>6mm): ❑Yes o ❑N/A 16. Trip Blank Present: Trip Blank Custody Seals Present Pace Trip Blank Lot #-(if purchased): - - - ❑Yes []No ❑Yes ❑No -- - ❑ /A /A -. -_ c;ltent Notification/ Resolution: Person Contacted: Comments/ Resolution: Date/Time: SCURF Review: 6 c Date: to-/ SRF Review: ([ j Date: U L �L Note: Whenever there is a discrepancy affecting North Carolina compliance samples, a copy of this form will be sent to the North Carolina DEHNR Certification Office ( i.e out of hold, Incorrect preservative, out of temp, Incorrect containers) Field Data Required? Y / N woo: szasa375" 1111111111111111111111 92252375 Page 10 of 11 ,. �FaceAnalytical" CHAIN -OF -CUSTODY / Analytical Request Document The Chain -of -Custody is a LEGAL DOCUMENT. All relevant fields must be completed accurately. 6 Section A Section B Section C Page: of Required Client Information: Required Project Information: Invoice Information: Company. n Report To: . Attention: 1902170 Address: J , Copy To: J Company Name: � 1 ` a„�.. �`• S.. ��' /r/G (��', j REGULATORY AGENCY Address. NPDES GROUND WATER r' DRINKING WATER !- UST r RCRA r OTHER Email To:3 �••� � LS c.A {fit AGa. Purchase Order No.: Paw Ouoto p . n �+ 3 C3, Phone: Fax 70�-- G'-KZ7 Project Name: �G i / r�P A — CC, Rataronw: �/ Q7-� Tt , Paw Pro as Site Requested Due DateITAT:✓ 1 f'i { �l Project Number. U��ys `Y : Manager Paw Prone # { t Location STATE: �fCr Requested Analysis Filtered {Y!N) Section D Matrix Codes m ~ Roqulred0lont Information MATRIX I CODE o o COLLECTED Pieservafives r T1 Drinking Water DW ct z Water WT Waste Water WW CM COMPOSITE COMPOSRE Product P SoiVSolid SL START ENDfGRAS W 0 V SAMPLE 1D Wipe WP = �? (Ad 0.9 / ;) Air AR Sample IOs MUST BE UNIQUE TS O IL F Q.? { W ~ a) y m o OtherTissue OT X � w w p m n 'o a C+ qt W 1_' Q 0 O. C, _ 0 rp L_ fU C V cc b y DATE TIME TIME w # C O 2 Z 2 Li 2 to Z r0N z a7 O `Q Pace Project No./ Lab I.D. 1 SS�vL tvl C7 !/DATE �i istela2 c; 2 3 4 5 6 7 8 9 10 11 12 ADDITIONAL COMMENTS 3PJNQUISHEDBYIAFFILIATION DATE 71ME ACC DBY14FFILIATION DATE TIME SAMPLE CONDITIONS -g J�-,i -i �i�s �FsF=� a 1 �l f e ORIGINAL SAMPLER NAME AND SIGNATURE O e 0— m > o o L) PRINT Name of SAMPLER: �v C a ,�,: 1� 4 E u m m v76 E SIGNATURE of SAMPLER: DATE Signed r� ) (MWDDIYY): - ev.15-MaY-2007 Appendix S TCE Concentration Trends hart hickman SMARTER ENVIRONMENTAL SOLUTIONS 120 100 80 60 40 20 Oct-95 TCE Concentration Trend in Near Source Area Well DMW-1 (µg/L) Jun-97 Feb-99 Oct-00 May-02 Jan-04 Sep-05 Apr-07 Dec-08 Aug-10 Apr-12 Nov-13 f—TCE —EOS Injection (Dec. 2012) Jul-15 200 150 100 50 Jul-98 TCE Concentration Trend in Downgradient Well DMW-6 (µg/L) Mar-00 Nov-01 Jun-03 Feb-05 Oct-06 Jun-08 Jan-10 Sep-11 May-13 Dec-14 tTCE -EOS Injection (Dec. 2012)